Chlorine
fullChlorine is the world's disinfectant and the most used oxidant in water treatment, with a WHO guideline for free chlorine, US maximum residual disinfectant levels, regulated by-products (trihalomethanes, haloacetic acids, chlorate, chlorite) and chloride as the major anion of every water.
Typical wastewaters
- chlorinated municipal wastewater effluent free and combined chlorine residual (HOCl, OCl⁻, chloramines) after a 5 to 20 mg/L disinfection dose, removed by sulfite before discharge
- power plant once-through cooling water and cooling tower blowdown free available chlorine from intermittent biofouling control, 0.5 mg/L maximum and 0.2 mg/L average, discharged for no more than two hours a day
- municipal sewage, industrial effluent and road de-icing runoff chloride Cl⁻, the stable end state, conservative
- pulp bleaching chlorate ClO₃⁻
- rocket fuel, fireworks and flare manufacture and use perchlorate ClO₄⁻, not removed by conventional treatment
- textile dyeing and finishing and leather tanning total chlorine measured during sampling and reported, no limit value
1 · Identity
- Symbol, number
- Cl, 17
- Oxidation states in water
- -1 chloride (Cl⁻, the stable end state of all chlorine chemistry in water); 0 molecular chlorine, present only below about pH 4 in dilute solution; +1 hypochlorous acid, hypochlorite and the inorganic chloramines (free and combined chlorine); +3 chlorite; +4 chlorine dioxide; +5 chlorate; +7 perchlorate.
- Note
- Free chlorine means HOCl plus OCl⁻; combined chlorine means the chloramines NH₂Cl, NHCl₂ and NCl₃ and organic chloramines; total chlorine is their sum. The element entry already carries the hydrolysis and bleach equations; this chapter extends them to the treatment plant.
2 · Occurrence in water
- Natural sources
- Chloride from halite and other evaporites, seawater (19,400 mg/L), saline intrusion and rain; no oxidised chlorine occurs naturally except perchlorate, which forms in the atmosphere and is deposited in rain and in arid soils and nitrate deposits (WHO perchlorate document).
- Anthropogenic sources
- Free chlorine from disinfection of drinking water, wastewater, swimming pools and cooling water; chloride from sewage, industrial effluent and de-icing salt (WHO); chlorate and perchlorate carried into water by aged hypochlorite and by chlorine dioxide generation; chlorate from pulp bleaching and herbicide use; perchlorate from rocket fuel, fireworks and flares (WHO); trihalomethanes and haloacetic acids formed when chlorine meets natural organic matter.
| matrix | typical range | note |
|---|---|---|
| disinfected drinking water, free chlorine | 0.2 to 1 mg/L | present in most disinfected drinking water at this level |
| seawater, chloride | 19,400 mg/L | oceanic abundance, Jefferson Lab via PubChem |
| municipal wastewater, chlorine dose for disinfection | 5 to 20 mg/L | applied dose; the residual is then removed by dechlorination before discharge |
| drinking water disinfected with hypochlorite, chlorate | median 99, 90th percentile 239, maximum 502 µg/LUS survey data | 1996 US Information Collection Rule survey; plants using chlorine dioxide: median 129, 90th percentile 264, maximum 691 µg/L; above 1 mg/L reported where hypochlorite was stored badly |
| drinking water, perchlorate | below 10 µg/Lregion-dependent | generally; concentrations above 40 µg/L have been measured |
| chlorinated drinking water, trihalomethanes | below 100 µg/L | generally; chloroform dominant unless bromide is present; not expected in raw water |
3 · Speciation
Chlorine gas hydrolyses at once to hypochlorous acid and chloride (equilibrium constant 3.94 x 10^4 per mol per litre at 25 C; complete above pH 3 in dilute solution). Hypochlorous acid is a weak acid, pKa 7.5 (7.6 in the EPA chloramine chapter): HOCl and OCl⁻ are equal at pH 7.5 and 25 C, HOCl dominates below pH 6.5 and OCl⁻ above pH 8.5. HOCl is the germicide, 70 to 80 times more effective than OCl⁻ against bacteria, so chlorination works best at lower pH. With ammonia, HOCl forms monochloramine below a Cl₂ to N weight ratio of 5 to 1, passes through the breakpoint between 5 to 1 and 7.6 to 1 where the residual falls to a minimum and nitrogen gas, nitrate and nitrogen trichloride form, and leaves free chlorine above 7.6 to 1; dichloramine dominates at low pH.
| condition | dominant species | note |
|---|---|---|
| chlorinated water, pH below 6.5 | HOCl | dissociation negligible; strongest disinfection |
| chlorinated water, pH 6.5 to 8.5 | HOCl and OCl⁻ together | equal at pH 7.5 and 25 C |
| chlorinated water, pH above 8.5 | OCl⁻ | hypochlorite stock solutions sit at about pH 12 |
| ammonia present, Cl₂ to N below 5 to 1 by weight, pH 7 to 8.5 | NH₂Cl monochloramine, with NHCl₂ at low pH | the chloramination window; utilities run Cl₂ to N at 3 to 1 to 5 to 1, typically 4 to 1, to avoid the breakpoint |
| ammonia present, Cl₂ to N above 7.6 to 1 | free chlorine plus NCl₃ | past the breakpoint; ammonia has been oxidised to N₂ and some nitrate |
| any water at equilibrium, and all effluent after dechlorination | Cl⁻ | chloride is the end state; free and combined chlorine are transient |
| aged hypochlorite solution | OCl⁻ with chlorite, chlorate and ultimately perchlorate | chlorite is a steady state intermediate between hypochlorite and chlorate; decomposition is faster warm and at high concentration, solid calcium hypochlorite decomposes much more slowly |
- Solubility
- Chlorine gas dissolves at 14.6 g/L at 0 C (WHO) but hydrolyses rather than staying as Cl₂. All chlorides of the common cations are freely soluble, so chloride is conservative: it passes every treatment except desalination. Chlorate and perchlorate salts are freely soluble and both anions are stable and mobile in water.
- Hydrolysis
- Cl₂ to HOCl and Cl⁻ with release of a proton, so chlorine gas lowers pH; sodium and calcium hypochlorite release hydroxide and raise it.
- Complexation
- Chloride forms weak complexes with metals (not quantified in the sources read) and raises the corrosion rate of metals in distribution systems, releasing metals into the supply (WHO chloride fact sheet).
- Precipitates
- None of significance for chloride, chlorate or perchlorate. AgCl is the analytical precipitate for chloride titration.
4 · Role in treatment
5 · Removal and control
- Efficiency
- to a non detectable residual
- Interferences
- excess sulfite, poor mixing; the balanced equation is written here from the sulfite equation the EPA prints
- Efficiency
- to a non detectable residual
- Interferences
- excess sulfite consumes oxygen
- Efficiency
- to a non detectable residual
- Efficiency
- to a non detectable residual
- Efficiency
- complete while capacity lasts
- Interferences
- organics compete for the carbon
- Efficiency
- below 0.1 mg/L
- Efficiency
- not applicable
- Interferences
- warm storage, high concentration stock
- Efficiency
- not quantified in the source
- Interferences
- sulfate and nitrate compete on non selective resins (general, not from the source read)
- Efficiency
- not quantified in the source
- Interferences
- bromide shifts products to brominated species
6 · Analytics
| method | standard | detection limit | note |
|---|---|---|---|
| DPD colorimetry, free and total chlorine | Standard Methods 4500-Cl G; ISO 7393-2; EPA 330.5 | 10 µg/L as free chlorine by colorimetry (WHO); ISO 7393-2 applies from about 0.03 to 5 mg/L Cl₂ | free chlorine read at once, total after iodide addition; combined by difference; the ZDHC method for total chlorine |
| amperometric titration | Standard Methods 4500-Cl D and E | about 0.02 mg/L (WHO background document, minimum detectable concentration) | separates free chlorine, monochloramine and dichloramine; unaffected by dichloramine in the 0 to 10 mg/L range (EPA) |
| iodometric titration | Standard Methods 4500-Cl B and C | for concentrations above 1 mg/L | for hypochlorite stock and high residuals |
| ion chromatography for chloride, chlorite and chlorate | EPA 300.1; Standard Methods 4500-Cl⁻ (chloride); ISO 10304 | chlorite 0.45 µg/L and chlorate 0.78 µg/L by IC with conductivity detection (WHO); chloride 200 µg/L by IC in the WHO chlorine sheet | |
| perchlorate | EPA 314.0 (IC, suppressed conductivity); EPA 331.0 (LC-MS) | EPA 314.0 reporting limit about 4 µg/L; LC-MS methods reach the ng/L range (WHO) | |
| trihalomethanes | purge and trap or liquid liquid extraction GC (EPA 524.2, 551.1) | not read this session | quench chlorine in the sample bottle or the reaction continues |
- Sampling pitfalls
- General practice, not from the sources read, except where noted: chlorine residual is measured on site at once: it is lost to light, agitation, warmth and reaction with the bottle contents. Samples for by-products need a quench (sulfite or ascorbic acid) or formation continues in the bottle. Chlorate and perchlorate samples need no preservation beyond cooling but hypochlorite stock must be diluted before injection. Chloride is conservative and easy; contamination from hands and glassware is the main error at low levels.
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), free chlorine | 5 mg/L | TDI 150 µg/kg body weight from a rodent NOAEL, 100 percent allocation to water; conservative, most people taste chlorine at this level; assessment 1993 |
| WHO GDWQ, chlorate | 0.7 mg/L | provisional; may be exceeded with aged hypochlorite or chlorine dioxide, and disinfection must never be compromised |
| WHO GDWQ, chlorite | 0.7 mg/L | provisional; chlorine dioxide itself has no guideline |
| WHO GDWQ, perchlorate | 70 µg/L | PMTDI 0.01 mg/kg body weight from a BMDL₅₀ of 0.11 mg/kg per day for iodide uptake inhibition |
| WHO GDWQ, trihalomethanes | chloroform 300; bromoform 100; dibromochloromethane 100; bromodichloromethane 60 µg/L | each individually |
| WHO GDWQ, chloride | no guideline | not of health concern; taste above about 250 mg/L; corrosion of metals in distribution |
| EU DWD 2020/2184, free chlorine | not set | Annex I has no parametric value for a disinfectant residual; Member States set it nationally; the Directive requires disinfection by-products to be kept as low as possible without compromising disinfection |
| EU DWD 2020/2184, chlorate | 0.25 mg/L | 0.70 mg/L where a disinfection method that generates chlorate, in particular chlorine dioxide, is used; measured only if such methods are used; Member States shall strive for a lower value |
| EU DWD 2020/2184, chlorite | 0.25 mg/L | 0.70 mg/L where chlorine dioxide is used; same conditions as chlorate |
| EU DWD 2020/2184, trihalomethanes total | 100 µg/L | sum of chloroform, bromoform, dibromochloromethane and bromodichloromethane; strive for a lower value |
| EU DWD 2020/2184, haloacetic acids | 60 µg/L | sum of mono-, di- and trichloroacetic acid and mono- and dibromoacetic acid; measured only when disinfection methods that can generate HAAs are used |
| EU DWD 2020/2184, chloride | 250 mg/L | Annex I Part C indicator parameter; the water should not be corrosive |
| EU DWD 2020/2184, perchlorate | not set | perchlorate is not in Annex I |
| US EPA NPDWR, chlorine (as Cl₂) | 4.0 mg/L | maximum residual disinfectant level (MRDL), MRDLG 4 |
| US EPA NPDWR, chloramines (as Cl₂) | 4.0 mg/L | MRDL, MRDLG 4 |
| US EPA NPDWR, chlorine dioxide (as ClO₂) | 0.8 mg/L | MRDL and MRDLG |
| US EPA NPDWR, chlorite | 1.0 mg/L | MCL; MCLG 0.8 |
| US EPA NPDWR, total trihalomethanes | 0.080 mg/L | MCL |
| US EPA NPDWR, haloacetic acids (HAA₅) | 0.060 mg/L | MCL |
| US EPA, chloride | 250 mg/L | secondary standard, salty taste |
| US EPA, chlorate | not regulated | monitored under UCMR 3; health reference level 210 µg/L in the third Six-Year Review; California notification level 800 µg/L and Health Canada 1 mg/L quoted there |
| US EPA, perchlorate | not regulated | 2020 withdrawal of the decision to regulate was vacated in 2023; proposed rule signed January 2026 with MCLG 0.02 mg/L and co-proposed MCL options of 20, 40 or 80 µg/L; final rule due by 21 May 2027 |
| body | limit | note |
|---|---|---|
| EU CWW BREF BAT-AEL (Decision 2016/902) | not set | free chlorine and chloride are not BAT 12 parameters; organically bound chlorine falls under AOX, 0.20 to 1.0 mg/L |
| US EPA 40 CFR 423.12(b)(6) and (7), steam electric once-through cooling water and cooling tower blowdown (BPT) | free available chlorine 0.5 maximum; 0.2 average mg/L | neither free available nor total residual chlorine may be discharged from any unit for more than two hours in any one day |
| US EPA 40 CFR 423.13(b)(1), once-through cooling water, plants of 25 MW and above (BAT) | total residual chlorine 0.20 maximum mg/L | cooling tower blowdown under 423.13(d)(1): free available chlorine 0.5 maximum, 0.2 average |
| Abu Dhabi ADS 23/2017, discharge to the marine environment (EAD) | free residual chlorine 0.5 mg/L region-dependent; marine discharge only | Table 1 maximum allowable concentration at the point of discharge; no chloride limit in the table |
| Abu Dhabi DoE Trade Effluent Control Regulations 2022, discharge to sewer | chloride 1000 mg/L region-dependent; sewer discharge | Table A₂; residual chlorine is not listed for sewer discharge |
| sector | body | limit | note |
|---|---|---|---|
| textile and leather | ZDHC Wastewater Guidelines v₂.1 (2022), total chlorine | sample and report only mg/L | conventional parameter measured during sampling by ISO 7393-2, EPA 330.5 or SM 4500-Cl G; no limit value |
8 · Health and environmental effects
- Toxicity
- Free chlorine at drinking water levels shows no specific adverse effects in humans or animals; TDI 150 µg/kg body weight; IARC places hypochlorite in Group 3 (WHO). Chlorine gas is another matter and is in the element entry. Chlorate and perchlorate act on the thyroid: chlorate ADI 0 to 0.01 mg/kg from thyroid effects in rats, perchlorate PMTDI 0.01 mg/kg from inhibition of iodide uptake (WHO). Chloroform and the brominated trihalomethanes carry individual guideline values (WHO).
- Bioaccumulation
- Not relevant for free and combined chlorine, which react to chloride within hours. Perchlorate is highly stable, poorly retained by soils (more than 90 percent stays in the water phase) and accumulates in arid soils; it is taken up by crops and appears in produce and milk (WHO perchlorate document).
- Ecotoxicity
- US EPA aquatic life criteria for chlorine: freshwater 19 µg/L acute and 11 µg/L chronic, saltwater 13 and 7.5 µg/L (1986). This is the basis of dechlorination requirements on chlorinated effluents and cooling water.
Flags
- The US perchlorate status is time sensitive: a proposed rule of January 2026 with a final rule due May 2027; check before reuse.
- The chlorate occurrence figures are a 1996 US survey quoted by WHO; European and GCC occurrence was not read.
- The breakpoint equation is balanced here from the EPA dose table (6.3 mg Cl₂ per mg NH₃), not copied from a printed equation.
- The hypochlorite decomposition stoichiometry (3 OCl⁻ to chlorate and chloride) is taken from the book's own element entry; the WHO 2016 document describes the pathway with chlorite as intermediate but prints no equation.
- The thiosulfate and activated carbon dechlorination equations are cited to Metcalf and Eddy chapter 12 and were not re-read this session.
- The chlorite reduction with Fe(II) is an electron balance; WHO names the reagent only.
- Abu Dhabi values cover two media (marine outfall free residual chlorine 0.5 mg/L; sewer chloride 1000 mg/L); other GCC states not read.
- The ISO 7393-2 working range is quoted from the ISO catalogue abstract, the standard itself was not read.
- No free chlorine parametric value exists at EU level; national values (for example the 0.1 to 0.5 mg/L residuals that many Member States require) were not read and are not quoted.
Gaps
- No source read gives chloride, free chlorine or chlorate concentrations in industrial wastewater; the CWW BREF text on free chlorine and AOX was not re-read.
- The WHO monochloramine guideline value and the WHO haloacetic acid values were not read (the 2022 fact sheet URLs returned 404); the US and EU values stand in.
- Detection limits for the trihalomethane methods were not read.
- Chloride removal (reverse osmosis, electrodialysis, evaporation) is not written up because no read source covers it; it belongs with the sodium and TDS chapters.
- Cyanide oxidation by alkaline chlorination and chlorine in cooling water biocide chemistry beyond the CFR limits were not sourced.
- No kinetic data for THM formation or for chlorate formation rates in hypochlorite beyond the qualitative WHO statements.
- EU national free chlorine residual requirements and other GCC states were not read.
Sources
WHO, Chlorine in Drinking-water, background document, WHO/SDE/WSH/03.04/45 (2003; text of 1996)
WHO GDWQ 4th ed. with addenda (2022), chapter 12 fact sheet, Chlorine dioxide, chlorite and chlorate (pp. 362 to 363)
WHO, Chlorine Dioxide, Chlorite and Chlorate in Drinking-water, background document, WHO/FWC/WSH/16.49 (2016), sections 1.4, 3 and 4
WHO GDWQ 4th ed. with addenda (2022), chapter 12 fact sheet, Perchlorate (pp. 450 to 451)
WHO, Perchlorate in Drinking-water, background document (2016), sections 1.4, 1.5, 4.1 and 4.2
WHO GDWQ 4th ed. with addenda (2022), chapter 12 fact sheet, Trihalomethanes (pp. 475 to 477)
WHO GDWQ 4th ed. with addenda (2022), chapter 12 fact sheet, Chloride (p. 361)
Directive (EU) 2020/2184 on the quality of water intended for human consumption (recast), Annex I Parts B and C
US EPA, National Primary Drinking Water Regulations (table of MCLs and MRDLs)
US EPA, Secondary Drinking Water Standards: Guidance for Nuisance Chemicals
US EPA, Six-Year Review 3 Technical Support Document for Chlorate, EPA-810-R-16-013 (December 2016)
US EPA, Perchlorate in Drinking Water (regulatory status page, read 2026-09-05)
US EPA, Alternative Disinfectants and Oxidants Guidance Manual, EPA 815-R-99-014 (April 1999), sections 2.2.3, 2.7.1, 4.1.1 and 6.1.1, Tables 2-7 and 6-1
US EPA, Wastewater Technology Fact Sheet: Chlorine Disinfection, EPA 832-F-99-062 (1999)
US EPA, Wastewater Technology Fact Sheet: Dechlorination, EPA 832-F-00-022 (September 2000)
US EPA, Arsenic Treatment Technology Design Manual for Small Systems, draft for peer review (June 2002), sections 2.4 and 2.7.3, Table 2-2
40 CFR 423.12, Effluent limitations guidelines representing BPT, steam electric power generating point source category
40 CFR 423.13, Effluent limitations guidelines representing BAT, 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
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 A2
ZDHC Wastewater Guidelines Version 2.1 (November 2022), conventional parameters table
US EPA, National Recommended Water Quality Criteria, Aquatic Life Criteria Table (chlorine, 1986)
Standard Methods for the Examination of Water and Wastewater (online edition), 4500-Cl Chlorine (Residual): B, C iodometric, D, E amperometric, F, G DPD
Standard Methods (online edition), 4500-Cl^- Chloride
ISO 7393-2:2017, Water quality. Determination of free chlorine and total chlorine. Part 2: Colorimetric method using N,N-dialkyl-1,4-phenylenediamine, for routine control purposes
PubChem element summary for chlorine; oceanic abundance 1.94 x 10^4 mg/L from Jefferson Lab
The Element Book, layer 1 entry for chlorine (data/elements/Cl.json), properties narrative: hypochlorite decay to chlorate
Metcalf and Eddy, Wastewater Engineering: Treatment and Resource Recovery, 5th ed. (McGraw-Hill, 2014), chapter 12 (disinfection processes, dechlorination)
Identity
- Name and symbol
- Chlorine, Cl
- Atomic number
- 17 protons
- Position
- group 17 · period 3 · p-block · diatomic nonmetal
- CAS number
- Cl₂: 7782-50-5
Atomic structure
- Atomic mass
- 35.4527 u
- Electron configuration
- 1s² 2s² 2p⁶ 3s² 3p⁵
[Ne] 3s²³p⁵ - Electrons per shell
- 2, 8, 7
- Valence electrons
- 7 outer shell
| isotope | mass (u) | abundance |
|---|---|---|
| 35Cl | 34.968852682(37) | 75.76 % |
| 37Cl | 36.965902602(55) | 24.24 % |
Physical properties
- State at room temperature
- Gas
- Melting point
- 171.65 K (-101.5 °C)
- Boiling point
- 239.11 K (-34.04 °C)
- Density
- 0.0032 g/cm3 (gas at STP, so 3.214 g/L)
- Appearance
- pale yellow-green gas
- Thermal conductivity
- 8.9-3 W/(m·K)
- Electrical resistivity
- >10 Ω·m at 20 °C
- Electrical conductivity
- 1.00e-1 S/m
- Crystal structure
- orthorhombic
- Molar heat capacity
- not in sources
Chemical properties
- Oxidation states
- +7, +5, +1, -1
- Electronegativity
- 3.16 (Pauling Scale)
- Ionisation energy
- 12.968 eV
1st 1,251.2, 2nd 2,298, 3rd 3,822 kJ/mol - Electron affinity
- 3.617 eV
- Atomic radius
- empirical 102, covalent 102, van der Waals 175 pm
- Ionic radius
- Cl⁻ 181; Cl⁵⁺ 12 (3py-coordinate); Cl⁷⁺ 27 pm
- Reactivity
- The second halogen ([Ne] 3s2 3p5), one electron short of an octet; a yellow-green gas that is one of the most reactive elements and a strong oxidiser, weaker than fluorine and stronger than bromine, combining directly with nearly all elements.
- with water
- Moderately soluble (about 3 volumes per volume at 10 C) and reacts reversibly and slowly to hydrochloric and hypochlorous acids, the basis of water disinfection:
- with oxygen, air
- Does not combine directly with oxygen; none of the chlorine oxides (Cl2O, ClO2, Cl2O7) can be made from the elements.
- with acids
- Does not react with acids; chlorine is itself liberated from hydrochloric acid by oxidisers such as manganese dioxide.
- with halogens
- Combines with fluorine to the interhalogens: chlorine monofluoride from the elements at 225 C, the trifluoride at 200 to 300 C and the pentafluoride with excess fluorine at 350 C and 250 atm:
- Typical compounds
- NaCl sodium chloride halite; brine electrolysis makes chlorine, hydrogen and caustic soda
- HCl hydrogen chloride hydrochloric acid; from burning hydrogen in chlorine
- NaOCl sodium hypochlorite bleach and disinfectant
- NaClO₃ sodium chlorate source of chlorine dioxide for pulp bleaching
- C₂H₃Cl vinyl chloride monomer of PVC, about a fifth of chlorine use
- CCl₄ carbon tetrachloride chlorinated solvent
Occurrence, production and use
- Crustal abundance
- 1.45×102 milligrams per kilogram
- Oceanic abundance
- 1.94×104 milligrams per liter
- Occurrence and sources
In nature it is found in the combined state only, chiefly with sodium as common salt (NaCl), carnallite, and sylvite.
- dissolved in seawater about 19,400 mg/L; crustal estimate 145 mg/kg (Jefferson Lab figures via PubChem)
- halite, rock salt (NaCl) and brine evaporite beds, salt domes, solution-mined brine and solar salt; the chemical industry took 39 percent of US salt in 2024, 91 percent of it as brine, chiefly for chlorine and caustic soda
- carnallite and sylvite (potassium chlorides) evaporite deposits
- Extraction, production
- Chlor-alkali electrolysis of brine (membrane, diaphragm or mercury cell)
Anode, all techniques: . Cathode, membrane and diaphragm cells: ; mercury cells form sodium amalgam and decompose it with water. Products come in fixed ratio, 1,070 to 1,128 kg NaOH and about 28 kg H2 per tonne Cl2. Side reactions in the anolyte make hypochlorite and chlorate and are repressed by low pH (CAK BREF, PDF p40). Mercury cells were about 6 to 7 percent of world capacity in 2012 (PDF p30).
- Uses
Chlorine is commonly used as an antiseptic and is used to make drinking water safe and to treat swimming pools. Large amounts of chlorine are used in many industrial processes, such as in the production of paper products, plastics, dyes, textiles, medicines, antiseptics, insecticides, solvents and paints.
Two of the most familiar chlorine compounds are sodium chloride (NaCl) and hydrogen chloride (HCl). Sodium chloride, commonly known as table salt, is used to season food and in some industrial processes. Hydrogen chloride, when mixed with water (H2O), forms hydrochloric acid, a strong and commercially important acid. Other chlorine compounds include: chloroform (CHCl3), carbon tetrachloride (CCl4), potassium chloride (KCl), lithium chloride (LiCl), magnesium chloride (MgCl2) and chlorine dioxide (ClO2).
Chlorine is a very dangerous material. Liquid chlorine burns the skin and gaseous chlorine irritates the mucus membranes. Concentrations of the gas as low as 3.5 parts per million can be detected by smell while concentrations of 1000 parts per million can be fatal after a few deep breaths.
Chlorine is widely used in making many everyday products. It is used for producing safe drinking water the world over. Even the smallest water supplies are now usually chlorinated.
It is also extensively used in the production of paper products, dyestuffs, textiles, petroleum products, medicines, antiseptics, insecticides, food, solvents, paints, plastics, and many other consumer products.
Most of the chlorine produced is used in the manufacture of chlorinated compounds for sanitation, pulp bleaching, disinfectants, and textile processing. Further use is in the manufacture of chlorates, chloroform, carbon tetrachloride, and in the extraction of bromine.
Organic chemistry demands much from chlorine, both as an oxidizing agent and in substitution, since it often brings many desired properties in an organic compound when substituted for hydrogen, as in one form of synthetic rubber.
- PVC: direct chlorination of ethylene, , -180 kJ/mol; EDC cracking, , +71 kJ/mol; oxychlorination that reuses the HCl, C2H4 + 1/2 , -239 kJ/mol; about 90 percent of plants run this balanced unit (LVOC BREF, PDF p528) PVC 33.3 percent (3,245 kt) of EU-27 and EFTA chlorine in 2012 (CAK BREF, PDF p31); the RSC's undated figure is about 20 percent
- Isocyanates, epichlorohydrin, chloromethanes and solvents: isocyanates and oxygenates for polyurethane foams, insulation and paints; epichlorohydrin for epoxy resins; chloromethanes for silicone rubbers and PTFE; phosphorus trichloride, p217); chlorinated solvents for degreasing and dry cleaning EU-27 and EFTA 2012: isocyanates and oxygenates 30.3 percent, other organics 9.3, epichlorohydrin 5.2, chloromethanes 4.6, solvents 2.9 (CAK BREF, PDF p31)
- Water treatment and disinfection: chlorination of drinking water and swimming pools worldwide; sodium hypochlorite from scrubbing chlorine in caustic; chlorine, hypochlorite and chlorine dioxide as oxidants in waste water treatment (CWW BREF, PDF p247) inorganics, including disinfectants, water treatment and pigments, 14.3 percent of EU-27 and EFTA chlorine in 2012
- Pharmaceuticals: chlorine as oxidant and in substitution reactions; 85 percent of pharmaceuticals use chlorine or its compounds at some stage
- Pulp, paper and textiles: pulp bleaching, textile processing, dyestuffs
- Safety, toxicity
Chlorine is a respiratory irritant. The gas irritates the mucus membranes and the liquid burns the skin. As little as 3.5 ppm can be detected as an odor, and 1000 ppm is likely to be fatal after a few deep breaths. In fact, chlorine was used as a war gas in 1915.
Exposure to chlorine should not exceed 0.5 ppm (8-hour time-weighted average - 40 hour week).
GHS classification, signal word Warning- H317 May cause an allergic skin reaction Sensitization, Skin
Discovery and name
- Discovered by
- Carl Wilhelm Scheele
- Discovered
- 1774
- First isolated
- not in sources
- Named by
- not in sources
- Origin of the name
- after the Ancient Greek χλωρός ("pale green") because of its colour
It is a member of the halogen (salt-forming) group of elements and is obtained from chlorides by the action of oxidizing agents and more often by electrolysis; it is a greenish-yellow gas, combining directly with nearly all elements. At 10°C one volume of water dissolves 3.10 volumes of chlorine, at 30°C only 1.77 volumes.
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.