Aluminum
fullAluminium is the base of the world's most used coagulants (alum, polyaluminium chloride, sodium aluminate), an EU indicator parameter at 200 µg/L and a US secondary standard, and the residual that every coagulation plant has to manage; its hydrolysis chemistry is the reason the coagulants work.
Typical wastewaters
- acid mine drainage dissolved Al³⁺ at extreme acidity, up to 90 mg/L; precipitates as Al(OH)₃ with iron when lime or limestone raises the pH to 6 to 7
- municipal wastewater dosed with aluminium salts for phosphorus removal AlPO₄ and Al(OH)₃ in the sludge, 1.5 to 3 times the theoretical 1 mol Al per mol P dosed
- alumina refining bauxite residue (red mud) leachate aluminate Al(OH)₄⁻ in pH 13 leachate; over 99 percent removed as a boehmite-like precipitate and dawsonite on HCl neutralisation, 86 percent with gypsum (calcite), over 99 percent with seawater (hydrotalcite) Ajka, Hungary spill leachate
- sulfuric acid anodising and caustic etching or chemical milling of aluminium Al³⁺ in spent sulfuric acid anodising electrolyte (5 to 10 g/L in service, bath dumped at 15 to 20 g/L) and sodium aluminate in caustic milling baths discarded above 70 g/L Al; sludge is Al(OH)₃ and NaAlO₂ STM BREF sections 4.11.3.1 and 2.5.23
- anodising plant mixed wastewater aluminium with iron, sulfate and COD in mixed anodic oxidation coating wastewater over 99 percent Al removal by PTFE membrane distillation
- aluminium forming (rolling, casting, quench cooling, cleaning and etching) aluminium in rolling emulsions, contact cooling water and cleaning or etching rinses BPT 49.55 mg/off-kg daily maximum for solution heat treatment contact cooling water, 0.525 mg/off-kg for rolling with neat oils
- secondary aluminium smelting (wet processing of dross and residues) aluminium with fluoride and ammonia in residue processing wastewater BPT 30-day average 1.0 kg/t product, fluoride 0.4 kg/t
- steel slag disposal drainage dissolved aluminium as aluminate in pH above 10 slag leachate rich in calcium and zinc 36 year dataset, northern England
1 · Identity
- Symbol, number
- Al, 13
- Oxidation states in water
- +3 only. Al³⁺ as the hexaaqua ion in acid water, hydrolysed stepwise to AlOH²⁺, Al(OH)₂⁺, solid Al(OH)₃ near neutral pH and the aluminate anion Al(OH)₄⁻ in alkaline water; polynuclear hydroxy cations in prehydrolysed coagulants; complexes with fluoride, sulfate, phosphate, silicate and natural organic matter.
- Note
- The element entry covers the ores, the smelter and the properties narrative already notes that the coagulants work by the same hydrolysis that makes acid soils toxic. This chapter is the water side: which aluminium species exists at which pH, how alum and PACl consume alkalinity, and what keeps residual aluminium below 0.1 mg/L.
2 · Occurrence in water
- Natural sources
- Weathering of aluminosilicates; dissolved aluminium is low near neutral pH because Al(OH)₃ caps it, and rises in acid waters (acid rain catchments, acid mine drainage, organic rich peat waters) where Al³⁺ and organic complexes are mobilised (WHO background document).
- Anthropogenic sources
- Carry over from aluminium coagulants is the main source in drinking water; acid mine drainage and metal pickling; alumina refinery red mud liquor and anodising rinse waters in the ledger's chemical and metals chapters (no concentration read for them here).
| matrix | typical range | note |
|---|---|---|
| natural water, near-neutral pH | 0.001 to 0.05 mg/L | dissolved aluminium |
| natural water, acidic or rich in organic matter | 0.5 to 1 mg/Lregion-dependent | |
| acid mine drainage | up to 90 mg/Lmaximum reported, no range | extreme acidity |
| drinking water, alum coagulation plants, USA | 0.01 to 1.3, average 0.16 mg/Lsurveys of the 1980s | treated water at facilities using aluminium sulfate; a second US survey of 186 supplies gave median 0.1 mg/L and maximum 2.7 mg/L at alum plants |
| drinking water, surface water plants using aluminium salts, Canada | mean 101 (provincial means 20 to 174) µg/L | total aluminium |
| seawater | 0.002 mg/Lsingle figure, no range | estimated oceanic abundance, Jefferson Lab figure via PubChem, as in the element entry |
3 · Speciation
Aluminium in water is a solubility story governed by pH. Below about pH 5 the hexaaqua Al³⁺ ion and its first hydrolysis products dominate and aluminium is dissolved and toxic to fish and plants; between about pH 5.5 and 7 amorphous Al(OH)₃ precipitates and dissolved aluminium is at its minimum (WHO puts the minimum in pure water at pH 5.5 to 6.0); above pH 7 to 8 the aluminate anion Al(OH)₄⁻ redissolves it. Fluoride, sulfate, phosphate, silicate and humic substances form complexes that keep aluminium in solution beyond what the hydroxide alone allows. Coagulation exploits the middle of the curve: alum or PACl dosed at pH 5 to 7 hydrolyses within seconds to positively charged hydroxy polymers and then to Al(OH)₃ floc.
| condition | dominant species | note |
|---|---|---|
| acid water, pH below 5 (acid rain lakes, mine drainage) | Al³⁺ (hexaaqua), AlOH²⁺, AlF²⁺, AlSO₄⁺, organic complexes | dissolved; the form toxic to fish gills and to plant roots in acid soils |
| pH 5.5 to 7, oxic | Al(OH)₃ (s), amorphous, ageing to gibbsite; Al(OH)₂⁺ and Al(OH)₄⁻ at trace level; Al bound to natural organic matter | minimum solubility; the coagulation window |
| alkaline water, pH above 8 | Al(OH)₄⁻ (aluminate) | dissolved again; the reason residual aluminium rises when coagulation pH drifts high and why lime softening plants can carry aluminate |
| prehydrolysed coagulant solution (PACl), pH 3 to 5 | polynuclear hydroxy aluminium cations, including the Al₁₃ polymer, and AlCl₃ hydrolysis products | the preformed polymers give PACl its charge neutralisation power at low dose and in cold water (MWH chapter 9, not re-read) |
- Solubility
- Controlled by amorphous Al(OH)₃ in fresh floc and by gibbsite in aged deposits; dissolved aluminium is lowest at pH 5.5 to 6.0 in pure water (WHO) and about 6 to 6.5 in natural water with sulfate and organic matter, rising on both sides. No solubility products are quoted because the sources read do not print them.
- Hydrolysis
- Al³⁺ hydrolyses stepwise, releasing one proton per step, to AlOH²⁺, Al(OH)₂⁺, Al(OH)₃ and Al(OH)₄⁻; the first hydrolysis constant is near pK 5 (Stumm and Morgan chapter 6, not re-read), so aluminium salts are acidic and every mole of alum dosed consumes six equivalents of alkalinity. Partial neutralisation before dosing (basicity, OH to Al ratio) is what distinguishes PACl from alum.
- Complexation
- Fluoride (AlF²⁺ and higher fluoro complexes), sulfate and phosphate as inorganic ligands; humic and fulvic acids as the organic ligands that hold aluminium in brown waters; silicate forms hydroxyaluminosilicates (WHO background document lists the ligands; constants not printed).
- Precipitates
- Al(OH)₃ (amorphous, then gibbsite), AlPO₄ (phosphorus removal), hydroxyaluminosilicates, basic aluminium sulfate in acid sulfate systems; Al(OH)₃ floc carries adsorbed arsenate, fluoride, phosphate and natural organic matter.
4 · Role in treatment
5 · Removal and control
- Efficiency
- 0.1 mg/L or less achievable in large plants under good operating conditions, 0.2 mg/L in small plants
- Interferences
- natural organic matter and fluoride hold aluminium in solution; cold water slows floc formation; high pH forms aluminate
- Efficiency
- not quoted in the sources read
- Interferences
- sulfate forms basic aluminium sulfates; re-dissolution if pH overshoots above 8.5
- Efficiency
- not quoted
- Interferences
- aluminium hydroxide fouls membranes when coagulant is overdosed ahead of them
6 · Analytics
| method | standard | detection limit | note |
|---|---|---|---|
| ICP-MS | EPA 200.8 (mass 27); ISO 17294-2 | EPA 200.8 instrument detection limit 0.05 µg/L scanning, 0.02 µg/L selected ion monitoring | total aluminium after acid digestion; dissolved after 0.45 µm filtration |
| ICP-OES | EPA 200.7 (308.215 nm); ISO 11885 | EPA 200.7 instrument detection limit 45 µg/L, total recoverable method detection limit 0.02 mg/L; WHO quotes 40 to 100 µg/L for ICP-AES | |
| graphite furnace AAS | ISO 15586 | working range 0.01 to 0.1 mg/L (WHO background document); flame AAS 5 to 100 mg/L | |
| eriochrome cyanine R colorimetry | Standard Methods 3500-Al B | not read | red to pink complex at pH 6.0 read at 535 nm; an EDTA-complexed portion serves as blank for colour and turbidity; ascorbic acid removes iron and manganese interference (method abstract) |
| pyrocatechol violet spectrometry | ISO 10566 (WHO cites ISO 1994) | 2 µg/L | measures aquated cations and forms readily converted to them by acidification |
- Sampling pitfalls
- Total, dissolved and reactive aluminium differ by an order of magnitude in coagulated water; filter 0.45 µm in the field for dissolved aluminium and state the fraction. Colloidal Al(OH)₃ settles and adheres to bottle walls, so acidify total aluminium samples at once. Speciation (labile monomeric versus organically bound) needs field separation, not read in the sources this session.
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 | a health-based value of 0.9 mg/L could be derived from the JECFA PTWI of 1 mg/kg body weight (20 percent allocation, 60 kg, 2 L/day) but exceeds practicable levels; practicable levels based on optimised coagulation are 0.1 mg/L or less in large plants and 0.2 mg/L or less in small ones; assessment 2009 |
| EU DWD 2020/2184 | 200 µg/L | Annex I Part C indicator parameter; uncertainty of measurement 25 percent of the parametric value (Annex III) |
| US EPA | 0.05 to 0.2 mg/L | National Secondary Drinking Water Regulation, non enforceable; effect listed as coloured water; aluminium is absent from the primary standards table |
| body | limit | note |
|---|---|---|
| EU CWW BREF BAT-AEL (Decision 2016/902) | not set | aluminium is not among the BAT 12 parameters |
| US EPA 40 CFR effluent guidelines | not set other categories not read | no aluminium limit in the metal finishing (433), steam electric (423), coal mining (434), textile (410) or tanning (425) sections read this session |
| Abu Dhabi ADS 23/2017, discharge to the marine environment (EAD) | 20 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 | 100 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 | aluminium is not a ZDHC wastewater parameter; the EU textiles BAT conclusions (2022) likewise list no aluminium BAT-AEL |
8 · Health and environmental effects
- Toxicity
- Little indication of acute oral toxicity; drinking water is usually under 5 percent of intake, food and antacids dominate. JECFA PTWI 1 mg/kg body weight (2007) for all aluminium compounds, expressed as a weekly value because of possible bioaccumulation. Epidemiological studies associating aluminium in drinking water above 100 µg/L with Alzheimer disease give relative risks below 2.0 and cannot be dismissed, but confounding and total intake were not controlled (WHO fact sheet, citing the 1997 EHC monograph).
- Bioaccumulation
- Absorption from water is usually less than 1 percent and depends on solubility, pH and speciation; JECFA kept a weekly rather than daily value because of the potential for accumulation (WHO).
- Ecotoxicity
- US EPA 2018 freshwater aquatic life criteria for aluminium vary with pH, total hardness and dissolved organic carbon: acute 1 to 4,800 µg/L and chronic 0.63 to 3,200 µg/L total recoverable aluminium, calculated per site; the 1988 fixed values were 750 µg/L acute and 87 µg/L chronic at pH 6.5 to 9.0. Acid water aluminium is the classic fish kill mechanism of acidified lakes.
Flags
- The occurrence figures for treated water are 1980s surveys quoted by the 2010 WHO background document; modern plants run lower.
- The seawater figure is a single PubChem abundance figure, not a range.
- The first hydrolysis constant (pK about 5), the PACl description and the membrane note are cited to textbook chapters from memory, not re-read this session.
- The alum alkalinity consumption (about 0.5 mg as CaCO₃ per mg alum 14-hydrate) is computed from the stoichiometry, not printed by a source read.
- The lime neutralisation equation for acid water is written here as the stoichiometry; the sources read describe neutralisation without printing it.
- The phosphorus precipitation ratio (1.5 to 3 times stoichiometric) is from Metcalf and Eddy chapter 6 by memory.
- Abu Dhabi values cover two media (marine 20 mg/L, sewer 100 mg/L) and differ five fold; other GCC states not read.
- The 2018 EPA aluminium criteria are site specific; the ranges quoted are the span of the calculator, not a single number.
Gaps
- No solubility product, hydrolysis constant table or complexation constants were read; Stumm and Morgan chapter 6 has them (from the chapter, not re-read).
- Alum sludge production and dewatering figures were not sourced.
- ISO 10566 is cited by number only; its catalogue page was not opened, so no url is given.
- The Standard Methods 3500-Al B detection limit was not read.
- Other GCC discharge standards (Saudi, Oman, Qatar) were not read.
- PACl basicity ranges and cold water performance are cited to MWH chapter 9 without re-reading; the Al₁₃ Keggin formula and the activated alumina ligand exchange are written from MWH chapters 9 and 16 on the same basis, from the chapter, not re-read, and no formation or surface constants were read.
- The caustic etch equation is standard amphoteric chemistry consistent with the book's own aluminium entry; no etch bath composition or spent liquor analysis was read.
Sources
WHO, Aluminium in Drinking-water, background document for development of WHO Guidelines for Drinking-water Quality, WHO/HSE/WSH/10.01/13 (2010), sections 1.5, 2.1, 6.1 and 6.2
Directive (EU) 2020/2184 on the quality of water intended for human consumption (recast), Annex I Parts B and C and Annex III
US EPA, Secondary Drinking Water Standards: Guidance for Nuisance Chemicals
US EPA, Arsenic Treatment Technology Design Manual for Small Systems, draft for peer review (June 2002), sections 2.5.2 (activated alumina, Table 2-3) and 2.7.1 (coagulation, optimum pH and doses)
US EPA, Final 2018 Aquatic Life Ambient Water Quality Criteria for Aluminum in Freshwater, fact sheet, Table 1
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 433.15, Pretreatment standards for existing sources (PSES), metal finishing 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 Tables A2 and A4
ZDHC Wastewater Guidelines Version 2.1 (November 2022), conventional parameters, anions and metals tables and sludge Table 4A
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)
US EPA Method 200.7, Revision 4.4 (1994), Determination of metals and trace elements in water and wastes by ICP-AES, Table 1 (wavelengths and instrument detection limits), Table 4 (method detection limits) and Table 5 (argon plasma conditions)
ISO 17294-2:2023, Water quality. Application of ICP-MS. Part 2: Determination of selected elements including uranium isotopes
ISO 11885:2007, Water quality. Determination of selected elements by inductively coupled plasma optical emission spectrometry (ICP-OES)
ISO 15586:2003, Water quality. Determination of trace elements using atomic absorption spectrometry with graphite furnace (Ag, Al, As, Cd, Co, Cr, Cu, Fe, Mn, Mo, Ni, Pb, Sb, Se, Tl, V, Zn)
Standard Methods for the Examination of Water and Wastewater (online edition), 3500-Al Aluminum (B. Eriochrome cyanine R method)
ISO 10566:1994, Water quality. Determination of aluminium. Spectrometric method using pyrocatechol violet (cited by WHO as ISO 1994; catalogue page not read)
PubChem element summary for aluminium; estimated oceanic abundance 2 x 10^-3 mg/L (PUG View, reference 5, Jefferson Lab)
The Element Book, layer 1 entry for aluminium (data/elements/Al.json and data/reference/text/Al.json)
Stumm, W. and Morgan, J. J., Aquatic Chemistry, 3rd ed. (Wiley, 1996), chapter 6 (metal ions in aqueous solution: hydrolysis of Al^3+) and chapter 7 (precipitation and dissolution)
Crittenden, J. C. et al., MWH's Water Treatment: Principles and Design, 3rd ed. (Wiley, 2012), chapter 9 (coagulation and flocculation: alum, PACl, alkalinity consumption) and chapter 12 (membrane filtration)
Metcalf and Eddy, Wastewater Engineering: Treatment and Resource Recovery, 5th ed. (McGraw-Hill, 2014), chapter 6 (chemical precipitation of phosphorus with aluminium)
Burke I. T., Peacock C. L., Lockwood C. L., Stewart D. I., Mortimer R. J., Ward M. B., Renforth P. and others, Behavior of aluminum, arsenic, and vanadium during the neutralization of red mud leachate by HCl, gypsum, or seawater, Environmental Science and Technology 47(12), 6527 to 6535 (2013), doi 10.1021/es4010834 (abstract)
EU Reference Document on Best Available Techniques for the Surface Treatment of Metals and Plastics (August 2006), section 2.5.23 chemical milling and section 4.11.3.1 retardation regeneration of sulphuric acid anodising solution (read from the Internet Archive copy of the EIPPCB PDF)
Turk O. K., Zoungrana A., Cakmakci M., Performances of PTFE and PVDF membranes in achieving the discharge limit of mixed anodic oxidation coating wastewaters treated by membrane distillation, Environmental Science and Pollution Research 31, 39663 to 39677 (2024), doi 10.1007/s11356-024-33830-9 (abstract)
40 CFR 467.12, Effluent limitations (BPT), aluminum forming point source category, Subpart A rolling with neat oils (core, continuous sheet casting, solution heat treatment contact cooling water, cleaning or etching)
40 CFR 421.32, Effluent limitations (BPT), nonferrous metals manufacturing point source category, Subpart C secondary aluminum smelting, paragraph (d) wet processing of residues
Riley A. L. and Mayes W. M., Long-term evolution of highly alkaline steel slag drainage waters, Environmental Monitoring and Assessment 187, 463 (2015), doi 10.1007/s10661-015-4693-1 (abstract)
Identity
- Name and symbol
- Aluminum, Al
- Atomic number
- 13 protons
- Position
- group 13 · period 3 · p-block · post-transition metal
- CAS number
- 7429-90-5
Atomic structure
- Atomic mass
- 26.981 u
- Electron configuration
- 1s² 2s² 2p⁶ 3s² 3p¹
[Ne] 3s²³p¹ - Electrons per shell
- 2, 8, 3
- Valence electrons
- 3 outer shell
| isotope | mass (u) | abundance |
|---|---|---|
| 27Al | 26.981 5384(3) | 100 % |
Physical properties
- State at room temperature
- Solid
- Melting point
- 933.44 K (660.29 °C)
- Boiling point
- 2,792 K (2,518.85 °C)
- Density
- 2.7 g/cm3
- Appearance
- Silvery gray metallic
- Thermal conductivity
- 237 W/(m·K)
- Electrical resistivity
- 26.5 nΩ·m at 20 °C
- Electrical conductivity
- 37.74 MS/m
- Crystal structure
- face-centered cubic
- Molar heat capacity
- 24.2 J/(mol·K)
Chemical properties
- Oxidation states
- +3
- Electronegativity
- 1.61 (Pauling Scale)
- Ionisation energy
- 5.986 eV
1st 577.5, 2nd 1,816.7, 3rd 2,744.8 kJ/mol - Electron affinity
- 0.441 eV
- Atomic radius
- empirical 121, covalent 121, van der Waals 184 pm
- Ionic radius
- Al³⁺ 54 pm
- Reactivity
- A post-transition metal of the boron group that forms +3 compounds and has a great affinity for oxygen; a self-healing oxide film about 5 nm thick makes the metal passive to air, water and dilute acids despite its high intrinsic reactivity.
- with water
- Does not react under ordinary conditions because of the oxide film; once the film is stripped (hot concentrated hydrochloric acid, alkali, amalgamation with mercury) aluminium reduces water to hydrogen.
- with oxygen, air
- Forms its protective oxide layer at once in air and corrodes no further; the fine powder burns brilliantly and reacts explosively with liquid oxygen, and the heat of oxide formation drives the thermite reaction:
- with acids
- Passive to dilute acids and to oxidising acids such as nitric and concentrated sulfuric, which are stored in aluminium; dissolves in hot concentrated hydrochloric acid with evolution of hydrogen, and in aqua regia:
- with halogens
- Reacts with the halogens on heating to the trihalides AlF3, AlCl3, AlBr3 and AlI3, Lewis acids used as Friedel-Crafts catalysts:
- Typical compounds
- Al₂O₃ aluminium oxide alumina; corundum, ruby, sapphire; feed for the smelter
- AlCl₃ aluminium chloride Lewis acid catalyst for Friedel-Crafts reactions
- Al(OH)₃ aluminium hydroxide amphoteric; water clarification, antacid
- Al₂(SO₄)₃ aluminium sulfate two thirds of it goes to water treatment
- KAl(SO₄)₂.12H₂O potash alum soluble double sulfate; mordant in dyeing
- Na₃AlF₆ cryolite molten electrolyte of the Hall-Heroult process
Occurrence, production and use
- Crustal abundance
- 8.23×104 milligrams per kilogram
- Oceanic abundance
- 2×10-3 milligrams per liter
- Occurrence and sources
The method of obtaining aluminum metal by the electrolysis of alumina dissolved in cryolite was discovered in 1886 by Hall in the U.S. and at about the same time by Heroult in France. Cryolite, a natural ore found in Greenland, is no longer widely used in commercial production, but has been replaced by an artificial mixture of sodium, aluminum, and calcium fluorides.
Aluminum can now be produced from clay, but the process is not economically feasible at present. Aluminum is the most abundant metal to be found in the earth's crust (8.1%), but is never found free in nature. In addition to the minerals mentioned above, it is also found in granite and in many other common minerals.
- dissolved in seawater about 0.002 mg/L; crustal estimate 82,300 mg/kg (Jefferson Lab figures via PubChem)
- bauxite (hydrated aluminium oxides) tropical laterites: Guinea, Australia, China, Brazil, Indonesia, India, Jamaica, Russia, Saudi Arabia, Vietnam; resources distributed Africa 32 percent, Oceania 23, South America and Caribbean 21, Asia 18
- clays, alunite, anorthosite, coal wastes, oil shales essentially inexhaustible subeconomic resources in most aluminium-producing countries; not competitive with bauxite
- cryolite, alum, feldspars and other aluminosilicates Greenland cryolite, now replaced by a synthetic fluoride bath; granite and most common rocks
- Extraction, production
- Bayer process: caustic digestion of bauxite to alumina
About 76 percent of bauxite consumed in the United States in 2024 was refined by the Bayer process to alumina or aluminium hydroxide; 69 percent of the alumina went to smelters and the rest to abrasives, ceramics, chemicals and refractories (USGS, printed pp. 42 to 43). Caustic soda for aluminium and metals was 6.0 percent of EU-27 and EFTA consumption in 2012 (CAK BREF, PDF p32). No equation is printed in the sources.
Hall-Heroult electrolysis of alumina dissolved in molten cryoliteAlumina is dissolved in a molten fluoride bath and reduced electrolytically to metal; aluminium fluoride and HF are key inputs and smelters recycle their fluorides (RSC; USGS fluorspar chapter). The reaction equation is not printed in the sources used.
Secondary aluminium from new and old scrapAbout 3.6 million tonnes recovered from purchased scrap in the United States in 2024, 56 percent new and 44 percent old scrap; old scrap alone equalled 37 percent of apparent consumption (USGS, printed pp. 32 to 33).
- Uses
Two important developments in the 1880s greatly increased the availability of aluminum. The first was the invention of a new process for obtaining aluminum from aluminum oxide. Charles Martin Hall, an American chemist, and Paul L. T. Héroult, a French chemist, each invented this process independently in 1886. The second was the invention of a new process that could cheaply obtain aluminum oxide from bauxite. Bauxite is an ore that contains a large amount of aluminum hydroxide (Al2O3·3H2O), along with other compounds. Karl Joseph Bayer, an Austrian chemist, developed this process in 1888. The Hall-Héroult and Bayer processes are still used today to produce nearly all of the world's aluminum.
With an easy way to extract aluminum from aluminum oxide and an easy way to extract large amounts of aluminum oxide from bauxite, the era of inexpensive aluminum had begun. In 1888, Hall formed the Pittsburgh Reduction Company, which is now known as the Aluminum Company of America, or Alcoa. When it opened, his company could produce about 25 kilograms of aluminum a day. By 1909, his company was producing about 41,000 kilograms of aluminum a day. As a result of this huge increase of supply, the price of aluminum fell rapidly to about $0.60 per kilogram.
Today, aluminum and aluminum alloys are used in a wide variety of products: cans, foils and kitchen utensils, as well as parts of airplanes, rockets and other items that require a strong, light material. Although it doesn't conduct electricity as well as copper, it is used in electrical transmission lines because of its light weight. It can be deposited on the surface of glass to make mirrors, where a thin layer of aluminum oxide quickly forms that acts as a protective coating. Aluminum oxide is also used to make synthetic rubies and sapphires for lasers.
It is extensively used for kitchen utensils, outside building decoration, and in thousands of industrial applications where a strong, light, easily constructed material is needed.
Although its electrical conductivity is only about 60% that of copper, it is used in electrical transmission lines because of its light weight. Pure aluminum is soft and lacks strength, but alloyed with small amounts of copper, magnesium, silicon, manganese, or other elements impart a variety of useful properties.
These alloys are of vital importance in the construction of modern aircraft and rockets. Aluminum, evaporated in a vacuum, forms a highly reflective coating for both visible light and radiant heat. These coatings soon form a thin layer of the protective oxide and do not deteriorate as do silver coatings. They are used to coat telescope mirrors and to make decorative paper, packages, and toys.
- Transport: alloys with copper, manganese, magnesium and silicon for aircraft, cars, trains and bicycles 36 percent of US aluminium consumption in 2024
- Packaging: cans, foil, beer kegs 23 percent of US consumption in 2024
- Construction and electrical: window frames and cladding; electrical transmission lines, cheaper than copper; vacuum-evaporated reflective coatings for mirrors and packaging building 14 percent, electrical 9 percent, consumer durables 8, machinery 8 of US consumption in 2024
- Chemicals: nonmetallurgical alumina for abrasives, ceramics, chemicals, proppants and refractories; aluminium sulfate and alum, the compounds of greatest importance after the oxide; aluminium fluoride from fluorspar or fluorosilicic acid
- Water treatment: alum, aluminium chloride, polyaluminium chloride and sulfate, and sodium aluminate as coagulants for colloids and suspended solids (CWW BREF, PDF p206 and p208)
- Textiles: alum as a dye mordant, a use as old as Greece and Rome
- Safety, toxicity
- GHS classification, signal word Danger
- H250 Catches fire spontaneously if exposed to air Pyrophoric liquids
- H261 In contact with water releases flammable gas Substances and mixtures which in contact with water, emit flammable gases
- H228 Flammable solid Flammable solids
- H370 Causes damage to organs Specific target organ toxicity, single exposure
- H372 Causes damage to organs through prolonged or repeated exposure Specific target organ toxicity, repeated exposure
Discovery and name
- Discovered by
- Hans Christian Ørsted
- Discovered
- 1824
- First isolated
- not in sources
- Named by
- Humphry Davy
- Origin of the name
- from alumine, obsolete name for alumina
Pure aluminum, a silvery-white metal, possesses many desirable characteristics. It is light, it is nonmagnetic and nonsparking, stands second among metals in the scale of malleability, and sixth in ductility.
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.