Zinc
fullZinc is the metal that galvanised pipe, brass fittings and corrosion inhibitors put into drinking water, a taste and acceptability parameter for WHO and the US EPA, a BAT-AEL metal in the EU chemical and textile sectors, and a routine effluent limit in metal finishing, mining and viscose.
Typical wastewaters
- chemical sector effluent (raw materials, plant corrosion, cooling water inhibitors) Zn²⁺ in metal bearing streams 5.6 to 250 mg/L before treatment, final effluent generally at or below 300 µg/L
- viscose rayon and acrylic fibre spinning Zn²⁺ from zinc sulfate spin baths and zinc chloride solvent; 6,796 (viscose) and 3,325 (acrylic) µg/L daily maximum
- electroplating and metal finishing total zinc 2.61 daily maximum and 1.48 mg/L monthly average
- mine drainage (copper, lead, zinc, gold, silver ores) Zn²⁺ in mine drainage, 1.5 daily maximum and 0.75 mg/L monthly average
- cooling tower blowdown (zinc corrosion inhibitors) Zn²⁺ from zinc based cooling water treatment, 1.0 mg/L total zinc
- municipal sewage (galvanised pipe corrosion, zinc orthophosphate) Zn²⁺ in sewage; urban wastewater treatment plants were the largest single source of zinc to water in the 2010 E-PRTR the WHO zinc document names corroding galvanised pipe and brass, and the EPA 2016 corrosion control guidance names zinc orthophosphate, as the loads behind it
- textile dyeing (zinc containing cationic dyes, viscose) total zinc 0.04 to 0.5 mg/L BAT-AEL, up to 0.8 mg/L with viscose fibres or zinc containing cationic dyes
1 · Identity
- Symbol, number
- Zn, 30
- Oxidation states in water
- +2 only, Zn²⁺ and its hydrolysis products, carbonate and sulfide solids; 0 as the sacrificial metal of galvanised steel and zinc anodes, which corrode to Zn²⁺.
- Note
- The element entry covers the ores, smelting and the amphoteric chemistry in outline; this chapter is the pipe, the effluent and the sludge.
2 · Occurrence in water
- Natural sources
- Weathering of sphalerite and other zinc sulfides; natural soil zinc 1 to 300 mg/kg; surface water usually below 10 µg/L and groundwater 10 to 40 µg/L (WHO background document).
- Anthropogenic sources
- Corrosion of galvanised iron pipe, brass and zinc alloy fittings, most in soft, acidic, carbon dioxide rich water (WHO); corrosion of plant pipework, tank insulation and roofs, raw materials, viscose fibre production and zinc based cooling water corrosion inhibitors in the chemical sector (CWW BREF section 2.4.3.9); zinc orthophosphate dosed for lead and copper control, which raises zinc loads to the sewage works (EPA OCCT 2016); electroplating and metal finishing, zinc and lead mine drainage, battery manufacture and cooling tower blowdown, each with its own US effluent limit. In the E-PRTR for 2010, 115 chemical installations emitted 150 t of zinc to water, 6 percent of a total of 2,513 t, and urban waste water treatment plants were the largest single source (CWW BREF section 1.2.3.11).
| matrix | typical range | note |
|---|---|---|
| surface water | below 10 µg/L | usually; the fact sheet says surface water normally does not exceed 0.01 mg/L |
| groundwater | 10 to 40 µg/L region-dependent; the well figure reflects corrosion and acid soils | normally not above 0.05 mg/L (fact sheet); up to 24 mg/L in a survey of almost 6,000 Finnish wells |
| tap water | below 20 (median) to 1.1 (maximum) µg/L to mg/Lsingle national survey | Finnish survey; the median is µg/L, the maximum 1.1 mg/L, from leaching of piping and fittings |
| seawater | 0.0049 mg/L single abundance figure, no range | estimated oceanic abundance, Jefferson Lab via PubChem |
| industrial wastewater, chemical sector final effluent | up to 300 µg/L | average effluent levels of directly discharging chemical WWTPs are generally at or below 300 µg/L; seven of 57 plants reported more, one of them from contaminated groundwater |
| industrial wastewater, metal bearing streams before treatment | 5.6 to 250 mg/L three plant examples, not a survey | 5.6 mg/L influent to one chemical plant pretreatment (Table 3.36); 50 to 250 mg/L feed to a crystallisation reactor (Table 3.40); 100 mg/L influent to a biological sulfide precipitation plant (Table 3.112) |
3 · Speciation
Zinc is Zn²⁺ over the whole natural pH range; hydrolysis to ZnOH⁺ begins only around pH 9, so free and ion paired zinc dominates in most waters. Its solids are Zn(OH)₂ and hydrozincite type basic carbonates in alkaline water, ZnCO₃ (smithsonite) in carbonate rich water, and ZnS in sulfidic sediments and anaerobic sludge, which holds zinc at very low solubility. The hydroxide is amphoteric and redissolves as zincate above about pH 11, so precipitation plants have a pH window on both sides.
| condition | dominant species | note |
|---|---|---|
| oxic or anoxic water, pH 5 to 8.5 | Zn²⁺, ZnSO₄ and ZnHCO₃⁺ ion pairs, zinc bound to natural organic matter and sorbed on iron and manganese oxides | no redox chemistry; solubility set by carbonate and sorption, not by oxidation state |
| alkaline water, pH 9 to 11 | ZnOH⁺, Zn(OH)₂ (s), basic zinc carbonate | the lime and caustic precipitation window; ZnCO₃ where carbonate is high |
| strong alkali, pH above about 11 | Zn(OH)₃⁻ and Zn(OH)₄²⁻ (zincate) | amphoteric redissolution; the reason overdosed lime leaks zinc (CWW BREF, amphoterism) |
| sulfidic, anaerobic sediment or sludge | ZnS (s) | the basis of sulfide precipitation and of biological sulfate reduction treatment |
| water in galvanised pipe | Zn²⁺ released from the zinc coating; basic zinc carbonate scale on the pipe wall | soft, acidic, carbon dioxide rich water is the most corrosive (WHO) |
- Solubility
- Zinc salts of the common anions (chloride, sulfate, nitrate) are freely soluble; Zn(OH)₂, ZnCO₃ and ZnS are the controlling solids. Chemical precipitation can reach about 1 to 10 mg/L for a single metal with lime and lower values with sulfide (CWW BREF citing VITO 2010); the solubility products themselves are not printed in the sources read.
- Hydrolysis
- Stepwise to ZnOH⁺, Zn(OH)₂, Zn(OH)₃⁻ and Zn(OH)₄²⁻; the first hydrolysis constant is near pK 9 (Stumm and Morgan chapter 6, from the chapter, not re-read), which is why zinc stays as the free ion in neutral water and why hydroxide precipitation needs pH 9 or more.
- Complexation
- Sulfate and bicarbonate ion pairs; natural organic matter; chelating agents such as EDTA keep zinc dissolved and make hydroxide precipitation incomplete (CWW BREF). Constants are not quoted because the sources read print none.
- Precipitates
- Zn(OH)₂, basic zinc carbonate (hydrozincite), ZnCO₃, ZnS; zinc phosphate on pipe walls where zinc orthophosphate is dosed.
4 · Role in treatment
5 · Removal and control
- Efficiency
- 5,600 to below 50 µg/L, 99 percent, at one chemical plant pretreatment (CWW BREF Table 3.36); achievable end concentrations for single metals with lime about 1 to 10 mg/L (VITO 2010 as cited)
- Interferences
- complexing agents, mixed metals with different optimum pH, carbonate and phosphate consuming reagent
- Efficiency
- biological removal 99.8 percent to 0.05 to 0.15 mg/L from 100 mg/L influent (CWW BREF Table 3.112); chemical sulfide reaches lower levels than hydroxide (BREF text)
- Interferences
- excess sulfide in the effluent; oxygen; the metal sulfide sludge
- Efficiency
- 1 mg/L zinc in the effluent
- Interferences
- suspended solids and complexing agents that stop pellet growth
- Efficiency
- not quoted
- Interferences
- calcium and magnesium compete; suspended solids foul the bed
- Efficiency
- not quoted
- Interferences
- zinc leached after treatment in the distribution system is untouched
- Efficiency
- about 50 to 90 percent at six chemical sector WWTPs (CWW BREF)
- Interferences
- inhibition above 5 to 20 mg/L
6 · Analytics
| method | standard | detection limit | note |
|---|---|---|---|
| flame AAS | ISO 8288; Standard Methods 3111 B | 50 µg/L direct air acetylene flame; 0.5 to 1 µg/L after chelation with APDC and extraction into MIBK (WHO background document) | the most widely used method in the WHO review |
| ICP-MS | EPA 200.8; ISO 17294-2; Standard Methods 3125 | EPA 200.8 instrument detection limit 0.2 µg/L scanning and 0.07 µg/L selected ion monitoring at mass 66; ICP-MS lower limit of application about 1 µg/L in the CWW BREF | the method named for ZDHC and CWW compliance monitoring (EN ISO 17294-2) |
| ICP-OES | EN ISO 11885; Standard Methods 3120 | limit of quantification about 1 µg/L (Germany, CWW BREF); Flanders treats zinc as not quantifiable below 25 µg/L and France sets the LOQ at 10 µg/L | the CWW BAT 4 monitoring standard for metals is any of the EN standards available |
| zincon colorimetry | Standard Methods 3500-Zn B | not read | field and small laboratory method; not read this session |
- Sampling pitfalls
- Galvanised fittings, brass taps and rubber tubing contaminate samples; distinguish first draw from flushed samples when the question is the pipe. Acidify to pH below 2 for total zinc; filter 0.45 µm in the field for dissolved zinc. Zinc is ubiquitous in laboratory dust and gloves, so blanks matter at the µg/L level.
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; JECFA PMTDI 1 mg/kg body weight (1982); assessment 1993 |
| WHO GDWQ, acceptability | 3 mg/L | above 3 mg/L water may not be acceptable to consumers (chapter 10 reference in the fact sheet); opalescence and greasy film above 3 to 5 mg/L |
| EU DWD 2020/2184 | not set | zinc is not a parameter of Annex I |
| US EPA | 5 mg/L | National Secondary Drinking Water Regulation, non enforceable; effect listed as metallic taste |
| US EPA health advisory (2018 table) | 2 mg/L | lifetime health advisory; one day and ten day 6 mg/L, RfD 0.3 mg/kg per day, DWEL 10 mg/L |
| body | limit | note |
|---|---|---|
| EU CWW BREF BAT-AEL (Decision 2016/902), direct discharge to a receiving water | 20 to 300 µg/L | yearly average, applies if the emission exceeds 30 kg/yr; lower end where little zinc is used or produced; may not apply to inorganic effluents from heavy metal compound production, to contaminated solid inorganic raw materials, or where the load comes from viscose fibre production (footnotes 24 to 26 and 29) |
| EU textiles BAT-AEL (Decision 2022/2508), all processes, direct and indirect discharge | 0.04 to 0.5 mg/L | upper end may be up to 0.8 mg/L when treating viscose fibres or dyeing with zinc containing cationic dyes (footnote 34) |
| US EPA 40 CFR 433.13, metal finishing (BPT) | 2.61 daily maximum; 1.48 monthly average mg/L total zinc | with cadmium 0.69 and 0.26, silver 0.43 and 0.24 mg/L |
| US EPA 40 CFR 414.91, OCPSF direct dischargers with biological treatment (BAT) | 2,610 daily maximum; 1,050 monthly average µg/L total zinc | viscose rayon 6,796 and 3,325 µg/L; zinc chloride solvent acrylic fibre 3,325 µg/L monthly; mass limits derived from metal bearing stream flows |
| US EPA 40 CFR 440.102(a), mine drainage from copper, lead, zinc, gold and silver mines (BPT) | 1.5 daily maximum; 0.75 30-day average mg/L | molybdenum ore mines 1.0 and 0.5 mg/L (paragraph (e)) |
| US EPA 40 CFR 423.13(d), steam electric cooling tower blowdown (BAT) | 1.0 mg/L total zinc | same value daily and 30-day; with total chromium 0.2 mg/L; for chemicals added for cooling tower maintenance |
| Abu Dhabi ADS 23/2017, discharge to the marine environment (EAD) | 0.5 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 | 1 mg/L region-dependent; sewer discharge, not receiving water | Table A₄ maximum allowable concentration for trade effluent to the sewer network; unusually, close to the marine value |
| sector | body | limit | note |
|---|---|---|---|
| textile and leather | ZDHC Wastewater Guidelines v₂.1 (2022), Table 2 | 5 foundational; 1 progressive; 0.5 aspirational mg/L | methods ISO 17294, EPA 200.8, 6010C, 6020A; zinc borate (Table 1N) reported as total zinc with a 100 µg/L reporting limit for textiles; sludge total zinc threshold 400 mg/kg dry weight (Table 4A) |
8 · Health and environmental effects
- Toxicity
- Essential: nearly 200 zinc enzymes; requirement 15 to 20 mg/day for adult men; JECFA PMTDI 1 mg/kg body weight. Acute: vomiting above about 500 mg zinc sulfate, mass poisonings from acidic drinks kept in galvanised containers; chronic excess causes copper deficiency (zinc therapy at 150 to 405 mg/day); no health based guideline value (WHO).
- Bioaccumulation
- Homeostatically regulated in animals, absorption 10 to 90 percent and biological half time about one year in humans (WHO); not a bioaccumulating contaminant in the mercury sense. Zinc toxicosis in livestock is copper deficiency.
- Ecotoxicity
- US EPA aquatic life criteria, dissolved zinc: freshwater 120 µg/L acute and 120 µg/L chronic at hardness 100 mg/L as CaCO₃ (hardness dependent, Appendix B equations), saltwater 90 and 81 µg/L (1995). Activated sludge inhibition threshold 5 to 20 mg/L (CWW BREF).
Flags
- The WHO concentration ranges are 1980s and 1990s compilations (Finnish surveys, Nriagu 1980); no recent survey was read.
- The seawater figure (4.9 µg/L) is a single abundance figure from Jefferson Lab via PubChem.
- The hydrolysis pK near 9 and the Zn(OH)₂ solubility minimum near pH 9.5 are cited to textbook chapters from memory, not re-read this session.
- The zincate, carbonate, sulfide and galvanised corrosion equations are electron and mass balances written here; the sources name the reactions but do not print them.
- CWW BREF Table 3.36 is one plant's pretreatment data and Tables 3.40 and 3.112 are single reference plants, not sector statistics.
- The activated sludge inhibition range 0.08 to 0.5 mg/L (UK Environment Agency 1997 as cited by the BREF) carries no rate reduction figure and conflicts with the 5 to 20 mg/L threshold of Table 3.115.
- Abu Dhabi values: marine outfall 0.5 mg/L, sewer 1 mg/L; other GCC states not read.
- EPA 2018 health advisory row for zinc read from a PDF table whose column alignment was verified against the cadmium row.
Gaps
- No source read gives zinc in municipal wastewater as a concentration; the CWW BREF only says urban WWTPs are the largest E-PRTR source.
- No solubility products or hydrolysis constants are printed in the sources read; Stumm and Morgan has them but was not re-read.
- No detection limit was read for the zincon method or for ISO 8288 beyond the WHO figure.
- Zinc in mine drainage and smelter effluent as concentrations is in the ledger's mining chapter, not here.
- Other GCC discharge standards (Saudi, Oman, Qatar) were not read.
- The reagent chemistry of zinc orthophosphate film formation is described by the EPA only in outline; the equation added here is the simple zinc phosphate solid, not a measured film composition.
- The hydrozincite, zinc anodic half reaction and EDTA chelation equations are from Stumm and Morgan chapters 6 and 8, from the chapter, not re-read; no stability constants, solubility products or electrode potentials beyond the standard zinc value were read.
Sources
WHO, Zinc in Drinking-water, background document for development of WHO Guidelines for Drinking-water Quality, WHO/SDE/WSH/03.04/17 (2003; text of 1996)
Directive (EU) 2020/2184 on the quality of water intended for human consumption (recast), Annex I Parts B and C and Annex III Table 1
US EPA, Secondary Drinking Water Standards: Guidance for Nuisance Chemicals
US EPA, 2018 Edition of the Drinking Water Standards and Health Advisories Tables, EPA 822-F-18-001 (March 2018)
US EPA, Optimal Corrosion Control Treatment Evaluation Technical Recommendations for Primacy Agencies and Public Water Systems, EPA 816-B-16-003 (March 2016), sections on orthophosphate and zinc orthophosphate inhibitors
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 4 and BAT 12 Table 3 with footnotes 24 to 29
Best Available Techniques Reference Document for Common Waste Water and Waste Gas Treatment/Management Systems in the Chemical Sector (CWW BREF 2016), sections 2.4.3.9 (zinc), 3.3.2.3.4.2 (chemical precipitation, Table 3.36), 3.3.2.3.4.3 (crystallisation, Table 3.40), 3.3.2.3.5.3 (biological removal of sulphur compounds and heavy metals, Table 3.112) and Table 3.115 (activated sludge inhibition thresholds)
Commission Implementing Decision (EU) 2022/2508 establishing BAT conclusions for the textiles industry, BAT 8 and Tables 1.3 and 1.4 (BAT-AELs for direct and indirect discharges) with footnotes 31, 34 and 41
40 CFR 433.13, Effluent limitations representing BPT, metal finishing point source category
40 CFR 414.91, Effluent limitations representing BAT, organic chemicals, plastics and synthetic fibers (OCPSF) direct discharge point sources that use end-of-pipe biological treatment
40 CFR 440.102, Effluent limitations representing BPT, ore mining and dressing, subpart J (copper, lead, zinc, gold, silver and molybdenum ores)
40 CFR 423.13, Effluent limitations guidelines representing BAT, steam electric power generating point source category (cooling tower blowdown, FGD wastewater, gasification wastewater)
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
ZDHC Wastewater Guidelines Version 2.1 (November 2022), Table 1M (organotins), Table 2 (heavy metals) and Tables 4A and 4B (sludge)
US EPA, National Recommended Water Quality Criteria, Aquatic Life Criteria Table and Appendix B (hardness equations)
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
ISO 17294-2:2023, Water quality. Application of ICP-MS. Part 2: Determination of selected elements including uranium isotopes
Standard Methods for the Examination of Water and Wastewater (online edition), 3111 Metals by Flame Atomic Absorption Spectrometry
Standard Methods (online edition), 3125 Metals by Inductively Coupled Plasma-Mass Spectrometry
Stumm, W. and Morgan, J. J., Aquatic Chemistry, 3rd ed. (Wiley, 1996), chapter 6 (metal ions in aqueous solution: hydrolysis and complexation) 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 heavy metals: hydroxide and sulfide solubility)
PubChem element summary for zinc; estimated oceanic abundance 4.9 x 10^-3 mg/L from Jefferson Lab
Identity
- Name and symbol
- Zinc, Zn
- Atomic number
- 30 protons
- Position
- group 12 · period 4 · d-block · transition metal
- CAS number
- 7440-66-6
Atomic structure
- Atomic mass
- 65.38 u
- Electron configuration
- 1s² 2s² 2p⁶ 3s² 3p⁶ 4s² 3d¹⁰
[Ar] 4s²³d¹⁰ - Electrons per shell
- 2, 8, 18, 2
- Valence electrons
- 12 ns and (n-1)d
| isotope | mass (u) | abundance |
|---|---|---|
| 64Zn | 63.929 142(5) | 49.17 % |
| 66Zn | 65.926 034(5) | 27.73 % |
| 67Zn | 66.927 127(5) | 4.04 % |
| 68Zn | 67.924 844(5) | 18.45 % |
| 70Zn | 69.925 32(2) | 0.61 % |
Physical properties
- State at room temperature
- Solid
- Melting point
- 692.68 K (419.53 °C)
- Boiling point
- 1,180 K (906.85 °C)
- Density
- 7.134 g/cm3
- Appearance
- silver-gray
- Thermal conductivity
- 116 W/(m·K)
- Electrical resistivity
- 59.0 nΩ·m at 20 °C
- Electrical conductivity
- 16.95 MS/m
- Crystal structure
- hexagonal close packed
- Molar heat capacity
- 25.47 J/(mol·K)
Chemical properties
- Oxidation states
- +2
- Electronegativity
- 1.65 (Pauling Scale)
- Ionisation energy
- 9.394 eV
1st 906.4, 2nd 1,733.3, 3rd 3,833 kJ/mol - Electron affinity
- 0 eV
- Atomic radius
- empirical 122, covalent 122, van der Waals 139 pm
- Ionic radius
- Zn²⁺ 74 pm
- Reactivity
- A group 12 metal ([Ar] 3d10 4s2) with a single +2 oxidation state and chemistry much like magnesium; a moderately reactive metal and strong reducing agent (E = -0.76 V), comparable to manganese, whose fresh surface tarnishes to a protective basic carbonate film.
- with water
- Does not react with cold water because the surface film of oxide and basic carbonate protects it.
- with oxygen, air
- Tarnishes quickly in air to a passivating layer of basic zinc carbonate; at high red heat it burns with a bright bluish-green flame to white clouds of zinc oxide:
- with acids
- Reacts readily with acids (and with alkalis to zincates); hydrochloric or sulfuric acid strips the passivating layer and then dissolves the metal with evolution of hydrogen, very pure zinc reacting only slowly:
- with halogens
- Reacts with all the halogens, violently with fluorine and with decreasing vigour down the group so that iodine gives only a little heat:
- Typical compounds
- ZnO zinc oxide white pigment, rubber, cosmetics; amphoteric
- ZnS zinc sulfide sphalerite, the main ore; luminous screens, lithopone
- ZnCO₃ zinc carbonate smithsonite ore; basic carbonate is the tarnish film
- ZnCl₂ zinc chloride important soluble salt; flux
- ZnSO₄ zinc sulfate soluble salt of the colourless Zn2+ ion
- Zn(C₂H₅)₂ diethylzinc pyrophoric organozinc reagent
Occurrence, production and use
- Crustal abundance
- 7.0×101 milligrams per kilogram
- Oceanic abundance
- 4.9×10-3 milligrams per liter
- Occurrence and sources
The principal ores of zinc are sphalerite (sulfide), smithsonite (carbonate), calamine (silicate), and franklinite (zinc, manganese, iron oxide). One method of zinc extraction involves roasting its ores to form the oxide and reducing the oxide with coal or carbon, with subsequent distillation of the metal.
- sphalerite or zinc blende (ZnS), smithsonite (ZnCO3), calamine (silicate), franklinite sulphide and oxidised zinc lead deposits; principal mining areas China, Australia and Peru, also India, Mexico, the United States, Bolivia, Kazakhstan, Russia and Sweden
- zinc concentrates carrying germanium and gallium Alaska and Tennessee zinc mines; germanium and gallium are recovered from zinc processing residues
- electric arc furnace dust and galvanising residues secondary zinc recovered as crude zinc oxide at smelters
- Extraction, production
- Roasting of sphalerite concentrate to zinc oxide
Balanced from the reactants and products stated by the sources: concentrate is roasted to the oxide (RSC, PubChem) and roasting metal sulphides releases the sulphur dioxide that non ferrous smelters turn into sulphuric acid (LVIC-AAF BREF).
Reduction of zinc oxide with carbon, or leaching and electrowinningThe equation given is the retort and imperial smelting reduction step, taken from the added secondary source. Refined production about 13.7 million tonnes in 2024 (estimate).
Zinc sulphide pigment by precipitationThe SIC BREF states that zinc sulphide and lithopone pigments are made from zinc sulphate and sodium sulphide; balanced from those reactants and the sulphide product, with sodium sulphate as the only possible co product. The ammonia plant desulphurisation step is stated verbatim by the LVIC-AAF BREF.
- Uses
Roughly one third of all metallic zinc produced today is used in a process known as galvanization. During galvanization, an object that is subject to corrosion, such as an iron nail, is given a protective coating of zinc. The zinc can be applied to an object by dipping it in a pool of molten zinc, but it is most often applied through an electroplating process. Sacrificial zinc anodes are used in cathodic protection systems to protect exposed iron from corrosion. Metallic zinc is also used to make dry cell batteries, roof cladding and die castings.
Zinc is used to make many useful alloys. Brass, an alloy of zinc that contains between 55% and 95% copper, is probably the best known zinc alloy. Brass was first used about 2,500 years ago and was widely used by the ancient Romans, who used it to make such things as coins, kettles and decorative items. Brass is still used today, particularly in musical instruments, screws and other hardware that must resist corrosion. Zinc is alloyed with lead and tin to make solder, a metal with a relatively low melting point used to join electrical components, pipes and other metallic items. Prestal®, an alloy containing 78% zinc and 22% aluminum, is a strange material that is nearly as strong as steel but is molded as easily as plastic. Nickel silver, typewriter metal, spring brass and German silver are other common zinc alloys.
Zinc oxide (ZnO), a common zinc compound, forms when metallic zinc is exposed to the air and forms a protective coating that protects the rest of the metal. Zinc oxide is used in paints, some rubber products, cosmetics, pharmaceuticals, plastics, printing inks, soap and batteries, among other things. Zinc sulfide (ZnS), another zinc compound, glows when it is exposed to ultraviolet light, X-rays or electrons and is used to make luminous watch dials, television screens and fluorescent light bulbs. Zinc chloride (ZnCl2) is another zinc compound that is used to protect wood from decay and insects.
The metal is employed to form numerous alloys with other metals. Brass, nickel silver, typewriter metal, commercial bronze, spring bronze, German silver, soft solder, and aluminum solder are some of the more important alloys.
Large quantities of zinc are used to produce die castings, which are used extensively by the automotive, electrical, and hardware industries. An alloy called Prestal(R), consisting of 78 percent zinc and 22 percent aluminum, is reported to be almost as strong as steel and as easy to mold as plastic. The alloy said to be so moldable that it can be molded into form using inexpensive ceramics or cement die casts.
Zinc is also used extensively to galvanize other metals such as iron to prevent corrosion. Zinc oxide is a unique and very useful material for modern civilization. It is widely used in the manufacture of paints, rubber products, cosmetics, pharmaceuticals, floor coverings, plastics, printing inks, soap, storage batteries, textiles, electrical equipment, and other products. Lithopone, a mixture of zinc sulfide and barium sulfate, is an important pigment.
Zinc sulfide is used in making luminous dials, X-ray and TV screens, and fluorescent lights.
The chloride and chromate are also important compounds. Zinc is an essential element in the growth of human beings and animals. Tests show that zinc-deficient animals require 50 percent more food to gain the same weight as an animal supplied with sufficient zinc.
- Galvanising and alloys: hot dip and electro galvanised steel for car bodies, lamp posts, barriers and bridges, the leading use of refined zinc; die casting alloys; brass, nickel silver and aluminium solder galvanised steel was the leading use of refined zinc in the United States in 2024, followed by brass and bronze and zinc base alloys (USGS, ranking only)
- Chemicals: zinc sulphate in the sulphuric acid spin bath that regenerates viscose fibre, leaving zinc hydroxide and zinc sulphide sludge; zinc sulphide and lithopone white pigments and zinc oxide; pelletised zinc oxide absorbing hydrogen sulphide from ammonia plant feed; copper oxide and zinc oxide shift catalyst; zinc stearate as the main mould release agent in polystyrene; zinc micronutrient in NPK fertilisers; zinc discharged from phosphoric acid, superphosphate, viscose, pigment and silicone plants
- Rubber, paint and consumer products: zinc oxide in paints, rubber, cosmetics, pharmaceuticals, plastics, inks, soaps, batteries and textiles; zinc sulphide in luminous paints and fluorescent lights
- Textiles: zinc borate as a flame retardant synergist; zinc is a compound in the textile chapter's discharge list
- Pharmaceuticals and fine chemicals: zinc among the heavy metals discharged from processes involving metals (OFC BREF)
- Mining: zinc ore is a base metal ore of the MWEI BREF; zinc is listed among substances discharged from base metal, precious metal, iron ore and bauxite extraction
- Safety, toxicity
Zinc is not considered to be toxic, but when freshly formed ZnO is inhaled a disorder known as oxide shakes or zinc chills sometimes occurs. Where zinc oxide is encountered, recommendations include providing good ventilation to avoid concentration exceeding 5 mg/m3, (time-weighted over an 8-hour exposure, 40-hour work week).
GHS classification, signal word Danger- H250 Catches fire spontaneously if exposed to air Pyrophoric liquids
- H260 In contact with water releases flammable gases which may ignite spontaneously Substances and mixtures which in contact with water, emit flammable gases
- H400 Very toxic to aquatic life Hazardous to the aquatic environment, acute hazard
- H410 Very toxic to aquatic life with long lasting effects Hazardous to the aquatic environment, long-term hazard
- H320 Causes eye irritation Serious eye damage/eye irritation
Discovery and name
- Discovered by
- Indian metallurgists
- Discovered
- before 1000 BC
- First isolated
- Andreas Sigismund Marggraf
- Named by
- not in sources
- Origin of the name
- probably from the German zinke, "tooth-like", since its crystals are needle-like
Zinc is a bluish-white, lustrous metal. It is brittle at ordinary temperatures but malleable at 100 to 150°C. It is a fair conductor of electricity, and burns in air at high red heat with evolution of white clouds of the oxide.
It exhibits superplasticity. Neither zinc nor zirconium is ferromagnetic; but ZrZn2 exhibits ferromagnetism at temperatures below 35°K. It has unusual electrical, thermal, optical, and solid-state properties that have not been fully investigated.
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.