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Chlorine, 17Cl
A glass container filled with yellow chlorine gas
Chlorine
Pronunciation/ˈklɔːrn, -n/ (KLOR-een, -⁠eyen)
Appearancepale yellow-green gas
Standard atomic weight Ar°(Cl)
Chlorine in the periodic table
Hydrogen Helium
Lithium Beryllium Boron Carbon Nitrogen Oxygen Fluorine Neon
Sodium Magnesium Aluminium Silicon Phosphorus Sulfur Chlorine Argon
Potassium Calcium Scandium Titanium Vanadium Chromium Manganese Iron Cobalt Nickel Copper Zinc Gallium Germanium Arsenic Selenium Bromine Krypton
Rubidium Strontium Yttrium Zirconium Niobium Molybdenum Technetium Ruthenium Rhodium Palladium Silver Cadmium Indium Tin Antimony Tellurium Iodine Xenon
Caesium Barium Lanthanum Cerium Praseodymium Neodymium Promethium Samarium Europium Gadolinium Terbium Dysprosium Holmium Erbium Thulium Ytterbium Lutetium Hafnium Tantalum Tungsten Rhenium Osmium Iridium Platinum Gold Mercury (element) Thallium Lead Bismuth Polonium Astatine Radon
Francium Radium Actinium Thorium Protactinium Uranium Neptunium Plutonium Americium Curium Berkelium Californium Einsteinium Fermium Mendelevium Nobelium Lawrencium Rutherfordium Dubnium Seaborgium Bohrium Hassium Meitnerium Darmstadtium Roentgenium Copernicium Nihonium Flerovium Moscovium Livermorium Tennessine Oganesson
F

Cl

Br
sulfurchlorineargon
Atomic number (Z)17
Groupgroup 17 (halogens)
Periodperiod 3
Block  p-block
Electron configuration[Ne] 3s2 3p5
Electrons per shell2, 8, 7
Physical properties
Phase at STPgas
Melting point(Cl2) 171.6 K ​(−101.5 °C, ​−150.7 °F)
Boiling point(Cl2) 239.11 K ​(−34.04 °C, ​−29.27 °F)
Density (at STP)3.2 g/L
when liquid (at b.p.)1.5625 g/cm3[3]
Triple point172.22 K, ​1.392 kPa[4]
Critical point416.9 K, 7.991 MPa
Heat of fusion(Cl2) 6.406 kJ/mol
Heat of vaporisation(Cl2) 20.41 kJ/mol
Molar heat capacity(Cl2)
33.949 J/(mol·K)
Vapour pressure
P (Pa) 1 10 100 1 k 10 k 100 k
at T (K) 128 139 153 170 197 239
Atomic properties
Oxidation statescommon: −1, +1, +3, +5, +7
+2,[5] +4,[5] +6[5]
ElectronegativityPauling scale: 3.16
Ionisation energies
  • 1st: 1251.2 kJ/mol
  • 2nd: 2298 kJ/mol
  • 3rd: 3822 kJ/mol
  • (more)
Covalent radius102±4 pm
Van der Waals radius175 pm
Color lines in a spectral range
Spectral lines of chlorine
Other properties
Natural occurrenceprimordial
Crystal structureorthorhombic (oS8)
Lattice constants
Orthorhombic crystal structure for chlorine
a = 630.80 pm
b = 455.83 pm
c = 815.49 pm (at triple point)[6]
Thermal conductivity8.9×10−3 W/(m⋅K)
Electrical resistivity>10 Ω⋅m (at 20 °C)
Magnetic orderingdiamagnetic[7]
Molar magnetic susceptibility−40.5×10−6 cm3/mol[8]
Speed of sound206 m/s (gas, at 0 °C)
CAS NumberCl2: 7782-50-5
History
Namingafter the Ancient Greek χλωρός ("pale green") because of its colour
Discovery and first isolationCarl Wilhelm Scheele (1774)
Recognized as an element byHumphry Davy (1808)
Isotopes of chlorine
Main isotopes[9] Decay
Isotope abun­dance half-life (t1/2) mode pro­duct
35Cl 75.8% stable
36Cl trace 3.01×105 y β 36Ar
ε 36S
37Cl 24.2% stable
 Category: Chlorine
| references

Chlorine is a chemical element; it has symbol Cl and atomic number 17. The second-lightest of the halogens, it appears between fluorine and bromine in the periodic table and its properties are mostly intermediate between them. Chlorine is a yellow-green gas at room temperature. It is an extremely reactive element and a strong oxidising agent: among the elements, it has the highest electron affinity and the third-highest electronegativity on the revised Pauling scale, behind only oxygen and fluorine.

Chlorine played an important role in the experiments conducted by medieval alchemists, which commonly involved the heating of chloride salts like ammonium chloride (sal ammoniac) and sodium chloride (common salt), producing various chemical substances containing chlorine such as hydrogen chloride, mercury(II) chloride (corrosive sublimate), and aqua regia. However, the nature of free chlorine gas as a separate substance was only recognised around 1630 by Jan Baptist van Helmont. Carl Wilhelm Scheele wrote a description of chlorine gas in 1774, supposing it to be an oxide of a new element. In 1809, chemists suggested that the gas might be a pure element, and this was confirmed by Sir Humphry Davy in 1810, who named it after the Ancient Greek χλωρός (khlōrós, "pale green") because of its colour.

Because of its great reactivity, all chlorine in the Earth's crust is in the form of ionic chloride compounds, which includes table salt. It is the second-most abundant halogen (after fluorine) and 20th most abundant element in Earth's crust. These crystal deposits are nevertheless dwarfed by the huge reserves of chloride in seawater.

Elemental chlorine is commercially produced from brine by electrolysis, predominantly in the chloralkali process. The high oxidising potential of elemental chlorine led to the development of commercial bleaches and disinfectants, and a reagent for many processes in the chemical industry. Chlorine is used in the manufacture of a wide range of consumer products, about two-thirds of them organic chemicals such as polyvinyl chloride (PVC), many intermediates for the production of plastics, and other end products which do not contain the element. As a common disinfectant, elemental chlorine and chlorine-generating compounds are used more directly in swimming pools to keep them sanitary. Elemental chlorine at high concentration is extremely dangerous, and poisonous to most living organisms. As a chemical warfare agent, chlorine was first used in World War I as a poison gas weapon.

In the form of chloride ions, chlorine is necessary to all known species of life. Other types of chlorine compounds are rare in living organisms, and artificially produced chlorinated organics range from inert to toxic. In the upper atmosphere, chlorine-containing organic molecules such as chlorofluorocarbons have been implicated in ozone depletion. Small quantities of elemental chlorine are generated by oxidation of chloride ions in neutrophils as part of an immune system response against bacteria.

History

[edit]

The most common compound of chlorine, sodium chloride, has been known since ancient times; archaeologists have found evidence that rock salt was used as early as 3000 BC and brine as early as 6000 BC.[10]

Early discoveries

[edit]

Around 900, the authors of the Arabic writings attributed to Jabir ibn Hayyan (Latin: Geber) and the Persian physician and alchemist Abu Bakr al-Razi (c. 865–925, Latin: Rhazes) were experimenting with sal ammoniac (ammonium chloride), which when it was distilled together with vitriol (hydrated sulfates of various metals) produced hydrogen chloride.[11] However, it appears that in these early experiments with chloride salts, the gaseous products were discarded, and hydrogen chloride may have been produced many times before it was discovered that it can be put to chemical use.[12] One of the first such uses was the synthesis of mercury(II) chloride (corrosive sublimate), whose production from the heating of mercury either with alum and ammonium chloride or with vitriol and sodium chloride was first described in the De aluminibus et salibus ("On Alums and Salts", an eleventh- or twelfth century Arabic text falsely attributed to Abu Bakr al-Razi and translated into Latin in the second half of the twelfth century by Gerard of Cremona, 1144–1187).[13] Another important development was the discovery by pseudo-Geber (in the De inventione veritatis, "On the Discovery of Truth", after c. 1300) that by adding ammonium chloride to nitric acid, a strong solvent capable of dissolving gold (i.e., aqua regia) could be produced.[14] Although aqua regia is an unstable mixture that continually gives off fumes containing free chlorine gas, this chlorine gas appears to have been ignored until c. 1630, when its nature as a separate gaseous substance was recognised by the Brabantian chemist and physician Jan Baptist van Helmont.[15][en 1]

Isolation

[edit]
Carl Wilhelm Scheele, discoverer of chlorine

The element was first studied in detail in 1774 by Swedish chemist Carl Wilhelm Scheele, and he is credited with the discovery.[16][17] Scheele produced chlorine by reacting MnO2 (as the mineral pyrolusite) with HCl:[15]

4 HCl + MnO2 → MnCl2 + 2 H2O + Cl2

Scheele observed several of the properties of chlorine: the bleaching effect on litmus, the deadly effect on insects, the yellow-green colour, and the smell similar to aqua regia.[18] He called it "dephlogisticated muriatic acid air" since it is a gas (then called "airs") and it came from hydrochloric acid (then known as "muriatic acid").[17] He failed to establish chlorine as an element.[17]

Common chemical theory at that time held that an acid is a compound that contains oxygen (remnants of this survive in the German and Dutch names of oxygen: sauerstoff or zuurstof, both translating into English as acid substance), so a number of chemists, including Claude Berthollet, suggested that Scheele's dephlogisticated muriatic acid air must be a combination of oxygen and the yet undiscovered element, muriaticum.[19][20]

In 1809, Joseph Louis Gay-Lussac and Louis-Jacques Thénard tried to decompose dephlogisticated muriatic acid air by reacting it with charcoal to release the free element muriaticum (and carbon dioxide).[17] They did not succeed and published a report in which they considered the possibility that dephlogisticated muriatic acid air is an element, but were not convinced.[21]

In 1810, Sir Humphry Davy tried the same experiment again, and concluded that the substance was an element, and not a compound.[17] He announced his results to the Royal Society on 15 November that year.[15] At that time, he named this new element "chlorine", from the Greek word χλωρος (chlōros, "green-yellow"), in reference to its colour.[22] The name "halogen", meaning "salt producer", was originally used for chlorine in 1811 by Johann Salomo Christoph Schweigger.[23] This term was later used as a generic term to describe all the elements in the chlorine family (fluorine, bromine, iodine), after a suggestion by Jöns Jakob Berzelius in 1826.[24][25] In 1823, Michael Faraday liquefied chlorine for the first time,[26][27][28] and demonstrated that what was then known as "solid chlorine" had a structure of chlorine hydrate (Cl2·H2O).[15]

Later uses

[edit]

Chlorine gas was first used by French chemist Claude Berthollet to bleach textiles in 1785.[29][30] Modern bleaches resulted from further work by Berthollet, who first produced sodium hypochlorite in 1789 in his laboratory in the town of Javel (now part of Paris, France), by passing chlorine gas through a solution of sodium carbonate. The resulting liquid, known as "Eau de Javel" ("Javel water"), was a weak solution of sodium hypochlorite. This process was not very efficient, and alternative production methods were sought. Scottish chemist and industrialist Charles Tennant first produced a solution of calcium hypochlorite ("chlorinated lime"), then solid calcium hypochlorite (bleaching powder).[29] These compounds produced low levels of elemental chlorine and could be more efficiently transported than sodium hypochlorite, which remained as dilute solutions because when purified to eliminate water, it became a dangerously powerful and unstable oxidiser. Near the end of the nineteenth century, E. S. Smith patented a method of sodium hypochlorite production involving electrolysis of brine to produce sodium hydroxide and chlorine gas, which then mixed to form sodium hypochlorite.[31] This is known as the chloralkali process, first introduced on an industrial scale in 1892, and now the source of most elemental chlorine and sodium hydroxide.[32] In 1884 Chemischen Fabrik Griesheim of Germany developed another chloralkali process which entered commercial production in 1888.[33]

Elemental chlorine solutions dissolved in chemically basic water (sodium and calcium hypochlorite) were first used as anti-putrefaction agents and disinfectants in the 1820s, in France, long before the establishment of the germ theory of disease. This practice was pioneered by Antoine-Germain Labarraque, who adapted Berthollet's "Javel water" bleach and other chlorine preparations.[34] Elemental chlorine has since served a continuous function in topical antisepsis (wound irrigation solutions and the like) and public sanitation, particularly in swimming and drinking water.[18]

Chlorine gas was first used as a weapon on 22 April 1915, at the Second Battle of Ypres by the German Army.[35][36] The effect on the allies was devastating because the existing gas masks were difficult to deploy and had not been broadly distributed.[37][38]

Properties

[edit]
Chlorine, liquefied under a pressure of 7.4 bar at room temperature, displayed in a quartz ampule embedded in acrylic glass
Gaseous chlorine stored inside a 500-mL water bottle. It is not recommended to store chlorine in this manner.
Solid chlorine at −150 °C

Chlorine is the second halogen, being a nonmetal in group 17 of the periodic table. Its properties are thus similar to fluorine, bromine, and iodine, and are largely intermediate between those of the first two. Chlorine has the electron configuration [Ne]3s23p5, with the seven electrons in the third and outermost shell acting as its valence electrons. Like all halogens, it is thus one electron short of a full octet, and is hence a strong oxidising agent, reacting with many elements in order to complete its outer shell.[39] Corresponding to periodic trends, it is intermediate in electronegativity between fluorine and bromine (F: 3.98, Cl: 3.16, Br: 2.96, I: 2.66), and is less reactive than fluorine and more reactive than bromine. It is also a weaker oxidising agent than fluorine, but a stronger one than bromine. Conversely, the chloride ion is a weaker reducing agent than bromide, but a stronger one than fluoride.[39] It is intermediate in atomic radius between fluorine and bromine, and this leads to many of its atomic properties similarly continuing the trend from iodine to bromine upward, such as first ionisation energy, electron affinity, enthalpy of dissociation of the X2 molecule (X = Cl, Br, I), ionic radius, and X–X bond length. (Fluorine is anomalous due to its small size.)[39]

All four stable halogens experience intermolecular van der Waals forces of attraction, and their strength increases together with the number of electrons among all homonuclear diatomic halogen molecules. Thus, the melting and boiling points of chlorine are intermediate between those of fluorine and bromine: chlorine melts at −101.0 °C and boils at −34.0 °C. As a result of the increasing molecular weight of the halogens down the group, the density and heats of fusion and vaporisation of chlorine are again intermediate between those of bromine and fluorine, although all their heats of vaporisation are fairly low (leading to high volatility) thanks to their diatomic molecular structure.[39] The halogens darken in colour as the group is descended: thus, while fluorine is a pale yellow gas, chlorine is distinctly yellow-green. This trend occurs because the wavelengths of visible light absorbed by the halogens increase down the group.[39] Specifically, the colour of a halogen, such as chlorine, results from the electron transition between the highest occupied antibonding πg molecular orbital and the lowest vacant antibonding σu molecular orbital.[40] The colour fades at low temperatures, so that solid chlorine at −195 °C is almost colourless.[39]

Like solid bromine and iodine, solid chlorine crystallises in the orthorhombic crystal system, in a layered lattice of Cl2 molecules. The Cl–Cl distance is 198 pm (close to the gaseous Cl–Cl distance of 199 pm) and the Cl···Cl distance between molecules is 332 pm within a layer and 382 pm between layers (compare the van der Waals radius of chlorine, 180 pm). This structure means that chlorine is a very poor conductor of electricity, and indeed its conductivity is so low as to be practically unmeasurable.[39]

Isotopes

[edit]

Chlorine has two stable isotopes, 35Cl and 37Cl. These are its only two natural isotopes occurring in quantity, with 35Cl making up 76% of natural chlorine and 37Cl making up the remaining 24%. Both are synthesised in stars in the oxygen-burning and silicon-burning processes.[41] Both have nuclear spin 3/2+ and thus may be used for nuclear magnetic resonance, although the spin magnitude being greater than 1/2 results in non-spherical nuclear charge distribution and thus resonance broadening as a result of a nonzero nuclear quadrupole moment and resultant quadrupolar relaxation. The other chlorine isotopes are all radioactive, with half-lives too short to occur in nature primordially. Of these, the most commonly used in the laboratory are 36Cl (t1/2 = 3.0×105 y) and 38Cl (t1/2 = 37.2 min), which may be produced from the neutron activation of natural chlorine.[39]

The most stable chlorine radioisotope is 36Cl. The primary decay mode of isotopes lighter than 35Cl is electron capture to isotopes of sulfur; that of isotopes heavier than 37Cl is beta decay to isotopes of argon; and 36Cl may decay by either mode to stable 36S or 36Ar.[42] 36Cl occurs in trace quantities in nature as a cosmogenic nuclide in a ratio of about (7–10) × 10−13 to 1 with stable chlorine isotopes: it is produced in the atmosphere by spallation of 36Ar by interactions with cosmic ray protons. In the top meter of the lithosphere, 36Cl is generated primarily by thermal neutron activation of 35Cl and spallation of 39K and 40Ca. In the subsurface environment, muon capture by 40Ca becomes more important as a way to generate 36Cl.[43][44]

Chemistry and compounds

[edit]
Halogen bond energies (kJ/mol)[40]
X XX HX BX3 AlX3 CX4
F 159 574 645 582 456
Cl 243 428 444 427 327
Br 193 363 368 360 272
I 151 294 272 285 239

Chlorine is intermediate in reactivity between fluorine and bromine, and is one of the most reactive elements. Chlorine is a weaker oxidising agent than fluorine but a stronger one than bromine or iodine. This can be seen from the standard electrode potentials of the X2/X couples (F, +2.866  V; Cl, +1.395 V; Br, +1.087  V; I, +0.615 V; At, approximately +0.3  V). However, this trend is not shown in the bond energies because fluorine is singular due to its small size, low polarisability, and inability to show hypervalence. As another difference, chlorine has a significant chemistry in positive oxidation states while fluorine does not. Chlorination often leads to higher oxidation states than bromination or iodination but lower oxidation states than fluorination. Chlorine tends to react with compounds including M–M, M–H, or M–C bonds to form M–Cl bonds.[40]

Given that E°(1/2O2/H2O) = +1.229 V, which is less than +1.395 V, it would be expected that chlorine should be able to oxidise water to oxygen and hydrochloric acid. However, the kinetics of this reaction are unfavorable, and there is also a bubble overpotential effect to consider, so that electrolysis of aqueous chloride solutions evolves chlorine gas and not oxygen gas, a fact that is very useful for the industrial production of chlorine.[45]

Hydrogen chloride

[edit]
Structure of solid deuterium chloride, with D···Cl hydrogen bonds

The simplest chlorine compound is hydrogen chloride, HCl, a major chemical in industry as well as in the laboratory, both as a gas and dissolved in water as hydrochloric acid. It is often produced by burning hydrogen gas in chlorine gas, or as a byproduct of chlorinating hydrocarbons. Another approach is to treat sodium chloride with concentrated sulfuric acid to produce hydrochloric acid, also known as the "salt-cake" process:[46]

NaCl + H2SO4 150 °C NaHSO4 + HCl
NaCl + NaHSO4 540–600 °C Na2SO4 + HCl

In the laboratory, hydrogen chloride gas may be made by drying the acid with concentrated sulfuric acid. Deuterium chloride, DCl, may be produced by reacting benzoyl chloride with heavy water (D2O).[46]

At room temperature, hydrogen chloride is a colourless gas, like all the hydrogen halides apart from hydrogen fluoride, since hydrogen cannot form strong hydrogen bonds to the larger electronegative chlorine atom; however, weak hydrogen bonding is present in solid crystalline hydrogen chloride at low temperatures, similar to the hydrogen fluoride structure, before disorder begins to prevail as the temperature is raised.[46] Hydrochloric acid is a strong acid (pKa = −7) because the hydrogen-chlorine bonds are too weak to inhibit dissociation. The HCl/H2O system has many hydrates HCl·nH2O for n = 1, 2, 3, 4, and 6. Beyond a 1:1 mixture of HCl and H2O, the system separates completely into two separate liquid phases. Hydrochloric acid forms an azeotrope with boiling point 108.58 °C at 20.22 g HCl per 100 g solution; thus hydrochloric acid cannot be concentrated beyond this point by distillation.[47]

Unlike hydrogen fluoride, anhydrous liquid hydrogen chloride is difficult to work with as a solvent, because its boiling point is low, it has a small liquid range, its dielectric constant is low and it does not dissociate appreciably into H2Cl+ and HCl
2
ions – the latter, in any case, are much less stable than the bifluoride ions (HF
2
) due to the very weak hydrogen bonding between hydrogen and chlorine, though its salts with very large and weakly polarising cations such as Cs+ and NR+
4
(R = Me, Et, Bun) may still be isolated. Anhydrous hydrogen chloride is a poor solvent, only able to dissolve small molecular compounds such as nitrosyl chloride and phenol, or salts with very low lattice energies such as tetraalkylammonium halides. It readily protonates nucleophiles containing lone-pairs or π bonds. Solvolysis, ligand replacement reactions, and oxidations are well-characterised in hydrogen chloride solution:[48]

Ph3SnCl + HCl ⟶ Ph2SnCl2 + PhH (solvolysis)
Ph3COH + 3 HCl ⟶ Ph
3
C+
HCl
2
+ H3O+Cl (solvolysis)
Me
4
N+
HCl
2
+ BCl3Me
4
N+
BCl
4
+ HCl (ligand replacement)
PCl3 + Cl2 + HCl ⟶ PCl+
4
HCl
2
(oxidation)

Other binary chlorides

[edit]
Hydrated nickel(II) chloride, NiCl2(H2O)6

Nearly all elements in the periodic table form binary chlorides. The exceptions are decidedly in the minority and stem in each case from one of three causes: extreme inertness and reluctance to participate in chemical reactions (the noble gases, with the exception of xenon in the highly unstable XeCl2 and XeCl4); extreme nuclear instability hampering chemical investigation before decay and transmutation (many of the heaviest elements beyond bismuth); and having an electronegativity higher than chlorine's (oxygen and fluorine) so that the resultant binary compounds are formally not chlorides but rather oxides or fluorides of chlorine.[49] Even though nitrogen in NCl3 is bearing a negative charge, the compound is usually called nitrogen trichloride.

Chlorination of metals with Cl2 usually leads to a higher oxidation state than bromination with Br2 when multiple oxidation states are available, such as in MoCl5 and MoBr3. Chlorides can be made by reaction of an element or its oxide, hydroxide, or carbonate with hydrochloric acid, and then dehydrated by mildly high temperatures combined with either low pressure or anhydrous hydrogen chloride gas. These methods work best when the chloride product is stable to hydrolysis; otherwise, the possibilities include high-temperature oxidative chlorination of the element with chlorine or hydrogen chloride, high-temperature chlorination of a metal oxide or other halide by chlorine, a volatile metal chloride, carbon tetrachloride, or an organic chloride. For instance, zirconium dioxide reacts with chlorine at standard conditions to produce zirconium tetrachloride, and uranium trioxide reacts with hexachloropropene when heated under reflux to give uranium tetrachloride. The second example also involves a reduction in oxidation state, which can also be achieved by reducing a higher chloride using hydrogen or a metal as a reducing agent. This may also be achieved by thermal decomposition or disproportionation as follows:[49]

EuCl3 + 1/2 H2 ⟶ EuCl2 + HCl
ReCl5 at "bp" ReCl3 + Cl2
AuCl3 160 °C AuCl + Cl2

Most metal chlorides with the metal in low oxidation states (+1 to +3) are ionic. Nonmetals tend to form covalent molecular chlorides, as do metals in high oxidation states from +3 and above. Both ionic and covalent chlorides are known for metals in oxidation state +3 (e.g. scandium chloride is mostly ionic, but aluminium chloride is not). Silver chloride is very insoluble in water and is thus often used as a qualitative test for chlorine.[49]

Polychlorine compounds

[edit]

Although dichlorine is a strong oxidising agent with a high first ionisation energy, it may be oxidised under extreme conditions to form the [Cl2]+ cation. This is very unstable and has only been characterised by its electronic band spectrum when produced in a low-pressure discharge tube. The yellow [Cl3]+ cation is more stable and may be produced as follows:[50]

Cl2 + ClF + AsF5 −78 °C [Cl3]+[AsF6]

This reaction is conducted in the oxidising solvent arsenic pentafluoride. The trichloride anion, [Cl3], has also been characterised; it is analogous to triiodide.[51]

Chlorine fluorides

[edit]

The three fluorides of chlorine form a subset of the interhalogen compounds, all of which are diamagnetic.[51] Some cationic and anionic derivatives are known, such as ClF
2
, ClF
4
, ClF+
2
, and Cl2F+.[52] Some pseudohalides of chlorine are also known, such as cyanogen chloride (ClCN, linear), chlorine cyanate (ClNCO), chlorine thiocyanate (ClSCN, unlike its oxygen counterpart), and chlorine azide (ClN3).[51]

Chlorine monofluoride (ClF) is extremely thermally stable, and is sold commercially in 500-gram steel lecture bottles. It is a colourless gas that melts at −155.6 °C and boils at −100.1 °C. It may be produced by the reaction of its elements at 225 °C, though it must then be separated and purified from chlorine trifluoride and its reactants. Its properties are mostly intermediate between those of chlorine and fluorine. It will react with many metals and nonmetals from room temperature and above, fluorinating them and liberating chlorine. It will also act as a chlorofluorinating agent, adding chlorine and fluorine across a multiple bond or by oxidation: for example, it will attack carbon monoxide to form carbonyl chlorofluoride, COFCl. It will react analogously with hexafluoroacetone, (CF3)2CO, with a potassium fluoride catalyst to produce heptafluoroisopropyl hypochlorite, (CF3)2CFOCl; with nitriles RCN to produce RCF2NCl2; and with the sulfur oxides SO2 and SO3 to produce ClSO2F and ClOSO2F respectively. It will also react exothermically with compounds containing –OH and –NH groups, such as water:[51]

H2O + 2 ClF ⟶ 2 HF + Cl2O

Chlorine trifluoride (ClF3) is a volatile colourless molecular liquid which melts at −76.3 °C and boils at 11.8  °C. It may be formed by directly fluorinating gaseous chlorine or chlorine monofluoride at 200–300 °C. One of the most reactive chemical compounds known, the list of elements it sets on fire is diverse, containing hydrogen, potassium, phosphorus, arsenic, antimony, sulfur, selenium, tellurium, bromine, iodine, and powdered molybdenum, tungsten, rhodium, iridium, and iron. It will also ignite water, along with many substances which in ordinary circumstances would be considered chemically inert such as asbestos, concrete, glass, and sand. When heated, it will even corrode noble metals as palladium, platinum, and gold, and even the noble gases xenon and radon do not escape fluorination. An impermeable fluoride layer is formed by sodium, magnesium, aluminium, zinc, tin, and silver, which may be removed by heating. Nickel, copper, and steel containers are usually used due to their great resistance to attack by chlorine trifluoride, stemming from the formation of an unreactive layer of metal fluoride. Its reaction with hydrazine to form hydrogen fluoride, nitrogen, and chlorine gases was used in experimental rocket engine, but has problems largely stemming from its extreme hypergolicity resulting in ignition without any measurable delay. Today, it is mostly used in nuclear fuel processing, to oxidise uranium to uranium hexafluoride for its enriching and to separate it from plutonium, as well as in the semiconductor industry, where it is used to clean chemical vapour deposition chambers.[53] It can act as a fluoride ion donor or acceptor (Lewis base or acid), although it does not dissociate appreciably into ClF+
2
and ClF
4
ions.[54]

Chlorine pentafluoride (ClF5) is made on a large scale by direct fluorination of chlorine with excess fluorine gas at 350 °C and 250 atm, and on a small scale by reacting metal chlorides with fluorine gas at 100–300 °C. It melts at −103 °C and boils at −13.1 °C. It is a very strong fluorinating agent, although it is still not as effective as chlorine trifluoride. Only a few specific stoichiometric reactions have been characterised. Arsenic pentafluoride and antimony pentafluoride form ionic adducts of the form [ClF4]+[MF6] (M = As, Sb) and water reacts vigorously as follows:[55]

2 H2O + ClF5 ⟶ 4 HF + FClO2

The product, chloryl fluoride, is one of the five known chlorine oxide fluorides. These range from the thermally unstable FClO to the chemically unreactive perchloryl fluoride (FClO3), the other three being FClO2, F3ClO, and F3ClO2. All five behave similarly to the chlorine fluorides, both structurally and chemically, and may act as Lewis acids or bases by gaining or losing fluoride ions respectively or as very strong oxidising and fluorinating agents.[56]

Chlorine oxides

[edit]
Yellow chlorine dioxide (ClO2) gas above a solution of hydrochloric acid and sodium chlorite in water, also containing dissolved chlorine dioxide
Structure of dichlorine heptoxide, Cl2O7, the most stable of the chlorine oxides

The chlorine oxides are well-studied in spite of their instability (all of them are endothermic compounds). They are important because they are produced when chlorofluorocarbons undergo photolysis in the upper atmosphere and cause the destruction of the ozone layer. None of them can be made from directly reacting the elements.[57]

Dichlorine monoxide (Cl2O) is a brownish-yellow gas (red-brown when solid or liquid) which may be obtained by reacting chlorine gas with yellow mercury(II) oxide. It is very soluble in water, in which it is in equilibrium with hypochlorous acid (HOCl), of which it is the anhydride. It is thus an effective bleach and is mostly used to make hypochlorites. It explodes on heating or sparking or in the presence of ammonia gas.[57]

Chlorine dioxide (ClO2) was the first chlorine oxide to be discovered in 1811 by Humphry Davy. It is a yellow paramagnetic gas (deep-red as a solid or liquid), as expected from its having an odd number of electrons: it is stable towards dimerisation due to the delocalisation of the unpaired electron. It explodes above −40 °C as a liquid and under pressure as a gas and therefore must be made at low concentrations for wood-pulp bleaching and water treatment. It is usually prepared by reducing a chlorate as follows:[57]

ClO
3
+ Cl + 2 H+ ⟶ ClO2 + 1/2 Cl2 + H2O

Its production is thus intimately linked to the redox reactions of the chlorine oxoacids. It is a strong oxidising agent, reacting with sulfur, phosphorus, phosphorus halides, and potassium borohydride. It dissolves exothermically in water to form dark-green solutions that very slowly decompose in the dark. Crystalline clathrate hydrates ClO2·nH2O (n ≈ 6–10) separate at low temperatures. However, in the presence of light, these solutions rapidly photodecompose to form a mixture of chloric and hydrochloric acids. Photolysis of individual ClO2 molecules result in the radicals ClO and ClOO, while at room temperature mostly chlorine, oxygen, and some ClO3 and Cl2O6 are produced. Cl2O3 is also produced when photolysing the solid at −78 °C: it is a dark brown solid that explodes below 0 °C. The ClO radical leads to the depletion of atmospheric ozone and is thus environmentally important as follows:[57]

Cl• + O3 ⟶ ClO• + O2
ClO• + O• ⟶ Cl• + O2

Chlorine perchlorate (ClOClO3) is a pale yellow liquid that is less stable than ClO2 and decomposes at room temperature to form chlorine, oxygen, and dichlorine hexoxide (Cl2O6).[57] Chlorine perchlorate may also be considered a chlorine derivative of perchloric acid (HOClO3), similar to the thermally unstable chlorine derivatives of other oxoacids: examples include chlorine nitrate (ClONO2, vigorously reactive and explosive), and chlorine fluorosulfate (ClOSO2F, more stable but still moisture-sensitive and highly reactive).[58] Dichlorine hexoxide is a dark-red liquid that freezes to form a solid which turns yellow at −180 °C: it is usually made by reaction of chlorine dioxide with oxygen. Despite attempts to rationalise it as the dimer of ClO3, it reacts more as though it were chloryl perchlorate, [ClO2]+[ClO4], which has been confirmed to be the correct structure of the solid. It hydrolyses in water to give a mixture of chloric and perchloric acids: the analogous reaction with anhydrous hydrogen fluoride does not proceed to completion.[57]

Dichlorine heptoxide (Cl2O7) is the anhydride of perchloric acid (HClO4) and can readily be obtained from it by dehydrating it with phosphoric acid at −10 °C and then distilling the product at −35 °C and 1 mmHg. It is a shock-sensitive, colourless oily liquid. It is the least reactive of the chlorine oxides, being the only one to not set organic materials on fire at room temperature. It may be dissolved in water to regenerate perchloric acid or in aqueous alkalis to regenerate perchlorates. However, it thermally decomposes explosively by breaking one of the central Cl–O bonds, producing the radicals ClO3 and ClO4 which immediately decompose to the elements through intermediate oxides.[57]

Chlorine oxoacids and oxyanions

[edit]
Standard reduction potentials for aqueous Cl species[45]
E°(couple) a(H+) = 1
(acid)
E°(couple) a(OH) = 1
(base)
Cl2/Cl +1.358 Cl2/Cl +1.358
HOCl/Cl +1.484 ClO/Cl +0.890
ClO
3
/Cl
+1.459
HOCl/Cl2 +1.630 ClO/Cl2 +0.421
HClO2/Cl2 +1.659
ClO
3
/Cl2
+1.468
ClO
4
/Cl2
+1.277
HClO2/HOCl +1.701 ClO
2
/ClO
+0.681
ClO
3
/ClO
+0.488
ClO
3
/HClO2
+1.181 ClO
3
/ClO
2
+0.295
ClO
4
/ClO
3
+1.201 ClO
4
/ClO
3
+0.374

Chlorine forms four oxoacids: hypochlorous acid (HOCl), chlorous acid (HOClO), chloric acid (HOClO2), and perchloric acid (HOClO3). As can be seen from the redox potentials given in the adjacent table, chlorine is much more stable towards disproportionation in acidic solutions than in alkaline solutions:[45]

Cl2 + H2O ⇌ HOCl + H+ + Cl Kac = 4.2 × 10−4 mol2 l−2
Cl2 + 2 OH ⇌ OCl + H2O + Cl Kalk = 7.5 × 1015 mol−1 l

The hypochlorite ions also disproportionate further to produce chloride and chlorate (3 ClO ⇌ 2 Cl + ClO
3
) but this reaction is quite slow at temperatures below 70 °C in spite of the very favourable equilibrium constant of 1027. The chlorate ions may themselves disproportionate to form chloride and perchlorate (4 ClO
3
⇌ Cl + 3 ClO
4
) but this is still very slow even at 100 °C despite the very favourable equilibrium constant of 1020. The rates of reaction for the chlorine oxyanions increases as the oxidation state of chlorine decreases. The strengths of the chlorine oxyacids increase very quickly as the oxidation state of chlorine increases due to the increasing delocalisation of charge over more and more oxygen atoms in their conjugate bases.[45]

Most of the chlorine oxoacids may be produced by exploiting these disproportionation reactions. Hypochlorous acid (HOCl) is highly reactive and quite unstable; its salts are mostly used for their bleaching and sterilising abilities. They are very strong oxidising agents, transferring an oxygen atom to most inorganic species. Chlorous acid (HOClO) is even more unstable and cannot be isolated or concentrated without decomposition: it is known from the decomposition of aqueous chlorine dioxide. However, sodium chlorite is a stable salt and is useful for bleaching and stripping textiles, as an oxidising agent, and as a source of chlorine dioxide. Chloric acid (HOClO2) is a strong acid that is quite stable in cold water up to 30% concentration, but on warming gives chlorine and chlorine dioxide. Evaporation under reduced pressure allows it to be concentrated further to about 40%, but then it decomposes to perchloric acid, chlorine, oxygen, water, and chlorine dioxide. Its most important salt is sodium chlorate, mostly used to make chlorine dioxide to bleach paper pulp. The decomposition of chlorate to chloride and oxygen is a common way to produce oxygen in the laboratory on a small scale. Chloride and chlorate may comproportionate to form chlorine as follows:[59]

ClO
3
+ 5 Cl + 6 H+ ⟶ 3 Cl2 + 3 H2O

Perchlorates and perchloric acid (HOClO3) are the most stable oxo-compounds of chlorine, in keeping with the fact that chlorine compounds are most stable when the chlorine atom is in its lowest (−1) or highest (+7) possible oxidation states. Perchloric acid and aqueous perchlorates are vigorous and sometimes violent oxidising agents when heated, in stark contrast to their mostly inactive nature at room temperature due to the high activation energies for these reactions for kinetic reasons. Perchlorates are made by electrolytically oxidising sodium chlorate, and perchloric acid is made by reacting anhydrous sodium perchlorate or barium perchlorate with concentrated hydrochloric acid, filtering away the chloride precipitated and distilling the filtrate to concentrate it. Anhydrous perchloric acid is a colourless mobile liquid that is sensitive to shock that explodes on contact with most organic compounds, sets hydrogen iodide and thionyl chloride on fire and even oxidises silver and gold. Although it is a weak ligand, weaker than water, a few compounds involving coordinated ClO
4
are known.[59] The Table below presents typical oxidation states for chlorine element as given in the secondary schools or colleges. There are more complex chemical compounds, the structure of which can only be explained using modern quantum chemical methods, for example, cluster technetium chloride [(CH3)4N]3[Tc6Cl14], in which 6 of the 14 chlorine atoms are formally divalent, and oxidation states are fractional.[60][61] In addition, all the above chemical regularities are valid for "normal" or close to normal conditions, while at ultra-high pressures (for example, in the cores of large planets), chlorine can form a Na3Cl compound with sodium, which does not fit into traditional concepts of chemistry.[62]

Chlorine oxidation state −1 +1 +3 +5 +7
Name chloride hypochlorite chlorite chlorate perchlorate
Formula Cl ClO ClO
2
ClO
3
ClO
4
Structure The chloride ion The hypochlorite ion The chlorite ion The chlorate ion The perchlorate ion

Organochlorine compounds

[edit]
Suggested mechanism for the chlorination of a carboxylic acid by phosphorus pentachloride to form an acyl chloride

Like the other carbon–halogen bonds, the C–Cl bond is a common functional group that forms part of core organic chemistry. Formally, compounds with this functional group may be considered organic derivatives of the chloride anion. Due to the difference of electronegativity between chlorine (3.16) and carbon (2.55), the carbon in a C–Cl bond is electron-deficient and thus electrophilic. Chlorination modifies the physical properties of hydrocarbons in several ways: chlorocarbons are typically denser than water due to the higher atomic weight of chlorine versus hydrogen, and aliphatic organochlorides are alkylating agents because chloride is a leaving group.[63]

Alkanes and aryl alkanes may be chlorinated under free-radical conditions, with UV light. However, the extent of chlorination is difficult to control: the reaction is not regioselective and often results in a mixture of various isomers with different degrees of chlorination, though this may be permissible if the products are easily separated. Aryl chlorides may be prepared by the Friedel-Crafts halogenation, using chlorine and a Lewis acid catalyst.[63] The haloform reaction, using chlorine and sodium hydroxide, is also able to generate alkyl halides from methyl ketones, and related compounds. Chlorine adds to the multiple bonds on alkenes and alkynes as well, giving di- or tetrachloro compounds. However, due to the expense and reactivity of chlorine, organochlorine compounds are more commonly produced by using hydrogen chloride, or with chlorinating agents such as phosphorus pentachloride (PCl5) or thionyl chloride (SOCl2). The last is very convenient in the laboratory because all side products are gaseous and do not have to be distilled out.[63]

Many organochlorine compounds have been isolated from natural sources ranging from bacteria to humans.[64][65] Chlorinated organic compounds are found in nearly every class of biomolecules including alkaloids, terpenes, amino acids, flavonoids, steroids, and fatty acids.[64][66] Organochlorides, including dioxins, are produced in the high temperature environment of forest fires, and dioxins have been found in the preserved ashes of lightning-ignited fires that predate synthetic dioxins.[67] In addition, a variety of simple chlorinated hydrocarbons including dichloromethane, chloroform, and carbon tetrachloride have been isolated from marine algae.[68] A majority of the chloromethane in the environment is produced naturally by biological decomposition, forest fires, and volcanoes.[69]

Some types of organochlorides, though not all, have significant toxicity to plants or animals, including humans. Dioxins, produced when organic matter is burned in the presence of chlorine, and some insecticides, such as DDT, are persistent organic pollutants which pose dangers when they are released into the environment. For example, DDT, which was widely used to control insects in the mid 20th century, also accumulates in food chains, and causes reproductive problems (e.g., eggshell thinning) in certain bird species.[70] Due to the ready homolytic fission of the C–Cl bond to create chlorine radicals in the upper atmosphere, chlorofluorocarbons have been discontinued due to the harm they do to the ozone layer.[57]

Occurrence

[edit]
Liquid chlorine analysis

Chlorine is too reactive to occur as the free element in nature but is very abundant in the form of its chloride salts. It is the 20th most abundant element[71] in Earth's crust and makes up 126 parts per million of it, through the large deposits of chloride minerals, especially sodium chloride, that have been evaporated from water bodies. All of these pale in comparison to the reserves of chloride ions in seawater: smaller amounts at higher concentrations occur in some inland seas and underground brine wells, such as the Great Salt Lake in Utah and the Dead Sea in Israel.[72]

Small batches of chlorine gas are prepared in the laboratory by combining hydrochloric acid and manganese dioxide, but the need rarely arises due to its ready availability. In industry, elemental chlorine is usually produced by the electrolysis of sodium chloride dissolved in water. This method, the chloralkali process industrialised in 1892, now provides most industrial chlorine gas.[32] Along with chlorine, the method yields hydrogen gas and sodium hydroxide, which is the most valuable product. The process proceeds according to the following chemical equation:[73]

2 NaCl + 2 H2O → Cl2 + H2 + 2 NaOH

Production

[edit]

Chlorine is primarily produced by the chloralkali process, although non-chloralkali processes exist. Global 2022 production was estimated to be 97 million tonnes.[74] The most visible use of chlorine is in water disinfection. 35–40 % of chlorine produced is used to make poly(vinyl chloride) through ethylene dichloride and vinyl chloride.[75] The chlorine produced is available in cylinders from sizes ranging from 450 g to 70 kg, as well as drums (865 kg), tank wagons (15 tonnes on roads; 27–90 tonnes by rail), and barges (600–1200 tonnes).[76] Due to the difficulty and hazards in transporting elemental chlorine, production is typically located near where it is consumed. As examples, vinyl chloride producers such as Westlake Chemical[77] and Formosa Plastics[78] have integrated chloralkali assets.

Chloralkali processes

[edit]

The electrolysis of chloride solutions all proceed according to the following equations:

Cathode: 2 H2O + 2 e → H2 + 2 OH
Anode: 2 Cl → Cl2 + 2 e

In the conventional case where sodium chloride is electrolysed, sodium hydroxide and chlorine are coproducts.

Industrially, there are three chloralkali processes:

  • The Castner–Kellner process that utilises a mercury electrode
  • The diaphragm cell process that utilises an asbestos diaphragm that separates the cathode and anode
  • The membrane cell process that uses an ion exchange membrane in place of the diaphragm

The Castner–Kellner process was the first method used at the end of the nineteenth century to produce chlorine on an industrial scale.[79][80] Mercury (that is toxic) was used as an electrode to amalgamate the sodium product, preventing undesirable side reactions.

In diaphragm cell electrolysis, an asbestos (or polymer-fiber) diaphragm separates a cathode and an anode, preventing the chlorine forming at the anode from re-mixing with the sodium hydroxide and the hydrogen formed at the cathode.[81] The salt solution (brine) is continuously fed to the anode compartment and flows through the diaphragm to the cathode compartment, where the caustic alkali is produced and the brine is partially depleted. Diaphragm methods produce dilute and slightly impure alkali, but they are not burdened with the problem of mercury disposal and they are more energy efficient.[32]

Membrane cell electrolysis employs permeable membrane as an ion exchanger. Saturated sodium (or potassium) chloride solution is passed through the anode compartment, leaving at a lower concentration. This method also produces very pure sodium (or potassium) hydroxide but has the disadvantage of requiring very pure brine at high concentrations.[82] However, due to the lower energy requirements of the membrane process, new chlor-alkali installations are now almost exclusively employing the membrane process. Next to this, the use of large volumes of mercury is considered undesirable. Also, older plants are converted into the membrane process.

Membrane cell process for chloralkali production

Non-chloralkali processes

[edit]

In the Deacon process, hydrogen chloride recovered from the production of organochlorine compounds is recovered as chlorine. The process relies on oxidation using oxygen:

4 HCl + O2 → 2 Cl2 + 2 H2O

The reaction requires a catalyst. As introduced by Deacon, early catalysts were based on copper. Commercial processes, such as the Mitsui MT-Chlorine Process, have switched to chromium and ruthenium-based catalysts.[83]

Applications

[edit]
A railway tank car carrying chlorine, displaying hazardous materials information including a diamond-shaped U.S. DOT placard showing a UN number[84]

Sodium chloride is the most common chlorine compound, and is the main source of chlorine for the demand by the chemical industry. About 15000 chlorine-containing compounds are commercially traded, including such diverse compounds as chlorinated methane, ethanes, vinyl chloride, polyvinyl chloride (PVC), aluminium trichloride for catalysis, the chlorides of magnesium, titanium, zirconium, and hafnium which are the precursors for producing the pure form of those elements.[18]

Quantitatively, of all elemental chlorine produced, about 63% is used in the manufacture of organic compounds, and 18% in the manufacture of inorganic chlorine compounds.[85] About 15,000 chlorine compounds are used commercially.[86] The remaining 19% of chlorine produced is used for bleaches and disinfection products.[76] The most significant of organic compounds in terms of production volume are 1,2-dichloroethane and vinyl chloride, intermediates in the production of PVC. Other particularly important organochlorines are methyl chloride, methylene chloride, chloroform, vinylidene chloride, trichloroethylene, perchloroethylene, allyl chloride, epichlorohydrin, chlorobenzene, dichlorobenzenes, and trichlorobenzenes. The major inorganic compounds include HCl, Cl2O, HOCl, NaClO3, AlCl3, SiCl4, SnCl4, PCl3, PCl5, POCl3, AsCl3, SbCl3, SbCl5, BiCl3, and ZnCl2.[76]

Sanitation, disinfection, and antisepsis

[edit]

Combating putrefaction

[edit]

In France (as elsewhere), animal intestines were processed to make musical instrument strings, Goldbeater's skin and other products. This was done in "gut factories" (boyauderies), and it was an odiferous and unhealthy process. In or about 1820, the Société d'encouragement pour l'industrie nationale offered a prize for the discovery of a method, chemical or mechanical, for separating the peritoneal membrane of animal intestines without putrefaction.[87][88] The prize was won by Antoine-Germain Labarraque, a 44-year-old French chemist and pharmacist who had discovered that Berthollet's chlorinated bleaching solutions ("Eau de Javel") not only destroyed the smell of putrefaction of animal tissue decomposition, but also actually retarded the decomposition.[88][34]

Labarraque's research resulted in the use of chlorides and hypochlorites of lime (calcium hypochlorite) and of sodium (sodium hypochlorite) in the boyauderies. The same chemicals were found to be useful in the routine disinfection and deodorisation of latrines, sewers, markets, abattoirs, anatomical theatres, and morgues.[89] They were successful in hospitals, lazarets, prisons, infirmaries (both on land and at sea), magnaneries, stables, cattle-sheds, etc.; and they were beneficial during exhumations,[90] embalming, outbreaks of epidemic disease, fever, and blackleg in cattle.[87]

Disinfection

[edit]

Labarraque's chlorinated lime and soda solutions have been advocated since 1828 to prevent infection (called "contagious infection", presumed to be transmitted by "miasmas"), and to treat putrefaction of existing wounds, including septic wounds.[91] In his 1828 work, Labarraque recommended that doctors breathe chlorine, wash their hands in chlorinated lime, and even sprinkle chlorinated lime about the patients' beds in cases of "contagious infection". In 1828, the contagion of infections was well known, even though the agency of the microbe was not discovered until more than half a century later.

During the Paris cholera outbreak of 1832, large quantities of so-called chloride of lime were used to disinfect the capital. This was not simply modern calcium chloride, but chlorine gas dissolved in lime-water (dilute calcium hydroxide) to form calcium hypochlorite (chlorinated lime). Labarraque's discovery helped to remove the terrible stench of decay from hospitals and dissecting rooms, and by doing so, effectively deodorised the Latin Quarter of Paris.[92] These "putrid miasmas" were thought by many to cause the spread of "contagion" and "infection" – both words used before the germ theory of infection. Chloride of lime was used for destroying odors and "putrid matter". One source claims chloride of lime was used by Dr. John Snow to disinfect water from the cholera-contaminated well that was feeding the Broad Street pump in 1854 London,[93] though three other reputable sources that describe that famous cholera epidemic do not mention the incident.[94][95][96] One reference makes it clear that chloride of lime was used to disinfect the offal and filth in the streets surrounding the Broad Street pump – a common practice in mid-nineteenth century England.[94]: 296 

Semmelweis and experiments with antisepsis

[edit]
Ignaz Semmelweis

Perhaps the most famous application of Labarraque's chlorine and chemical base solutions was in 1847, when Ignaz Semmelweis used chlorine-water (chlorine dissolved in pure water, which was cheaper than chlorinated lime solutions) to disinfect the hands of Austrian doctors, which Semmelweis noticed still carried the stench of decomposition from the dissection rooms to the patient examination rooms. Long before the germ theory of disease, Semmelweis theorised that "cadaveric particles" were transmitting decay from fresh medical cadavers to living patients, and he used the well-known "Labarraque's solutions" as the only known method to remove the smell of decay and tissue decomposition (which he found that soap did not). The solutions proved to be far more effective antiseptics than soap (Semmelweis was also aware of their greater efficacy, but not the reason), and this resulted in Semmelweis's celebrated success in stopping the transmission of childbed fever ("puerperal fever") in the maternity wards of Vienna General Hospital in Austria in 1847.[97]

Much later, during World War I in 1916, a standardised and diluted modification of Labarraque's solution containing hypochlorite (0.5%) and boric acid as an acidic stabiliser was developed by Henry Drysdale Dakin (who gave full credit to Labarraque's prior work in this area). Called Dakin's solution, the method of wound irrigation with chlorinated solutions allowed antiseptic treatment of a wide variety of open wounds, long before the modern antibiotic era. A modified version of this solution continues to be employed in wound irrigation in modern times, where it remains effective against bacteria that are resistant to multiple antibiotics.[98]

Public sanitation

[edit]
Chlorinated water is used in swimming pools to disinfect water from microbial contaminants
Liquid pool chlorine

The first continuous application of chlorination to drinking U.S. water was installed in Jersey City, New Jersey, in 1908.[99] By 1918, the US Department of Treasury called for all drinking water to be disinfected with chlorine. Chlorine is presently an important chemical for water purification (such as in water treatment plants), in disinfectants, and in bleach. Even small water supplies are now routinely chlorinated.[100]

Chlorine is usually used (in the form of hypochlorous acid) to kill bacteria and other microbes in drinking water supplies and public swimming pools. In most private swimming pools, chlorine itself is not used, but rather sodium hypochlorite, formed from chlorine and sodium hydroxide, or solid tablets of chlorinated isocyanurates. The drawback of using chlorine in swimming pools is that the chlorine reacts with the amino acids in proteins in human hair and skin. Contrary to popular belief, the distinctive "chlorine aroma" associated with swimming pools is not the result of elemental chlorine itself, but of chloramine, a chemical compound produced by the reaction of free dissolved chlorine with amines in organic substances including those in urine and sweat.[101] As a disinfectant in water, chlorine is more than three times as effective against Escherichia coli as bromine, and more than six times as effective as iodine.[102] Increasingly, monochloramine itself is being directly added to drinking water for purposes of disinfection, a process known as chloramination.[103]

It is often impractical to store and use poisonous chlorine gas for water treatment, so alternative methods of adding chlorine are used. These include hypochlorite solutions, which gradually release chlorine into the water, and compounds like sodium dichloro-s-triazinetrione (dihydrate or anhydrous), sometimes referred to as "dichlor", and trichloro-s-triazinetrione, sometimes referred to as "trichlor". These compounds are stable while solid and may be used in powdered, granular, or tablet form. When added in small amounts to pool water or industrial water systems, the chlorine atoms hydrolyse from the rest of the molecule, forming hypochlorous acid (HOCl), which acts as a general biocide, killing germs, microorganisms, algae, and so on.[104][105]

Use as a weapon

[edit]

World War I

[edit]

Chlorine gas, also known as bertholite, was first used as a weapon in World War I by Germany on 22 April 1915, in the Second Battle of Ypres.[106][107] As described by the soldiers, it had the distinctive smell of a mixture of pepper and pineapple.[108] It also tasted metallic and stung the back of the throat and chest. Chlorine reacts with water in the mucosa of the lungs to form hydrochloric acid, destructive to living tissue and potentially lethal. Human respiratory systems can be protected from chlorine gas by gas masks with activated charcoal or other filters, which makes chlorine gas much less lethal than other chemical weapons. It was pioneered by a German scientist later to be a Nobel laureate, Fritz Haber of the Kaiser Wilhelm Institute in Berlin, in collaboration with the German chemical conglomerate IG Farben, which developed methods for discharging chlorine gas against an entrenched enemy.[109] After its first use, both sides in the conflict used chlorine as a chemical weapon, but it was soon replaced by the more deadly phosgene and more debilitating mustard gas.[110]

Middle east

[edit]

Chlorine gas was also used during the Iraq War in Anbar Province in 2007, with insurgents packing truck bombs with mortar shells and chlorine tanks. The attacks killed two people from the explosives and sickened more than 350. Most of the deaths were caused by the force of the explosions rather than the effects of chlorine since the toxic gas is readily dispersed and diluted in the atmosphere by the blast. In some bombings, over a hundred civilians were hospitalised due to breathing difficulties. The Iraqi authorities tightened security for elemental chlorine, which is essential for providing safe drinking water to the population.[111][112]

On 23 October 2014, it was reported that the Islamic State of Iraq and the Levant had used chlorine gas in the town of Duluiyah, Iraq.[113] Laboratory analysis of clothing and soil samples confirmed the use of chlorine gas against Kurdish Peshmerga Forces in a vehicle-borne improvised explosive device attack on 23 January 2015 at the Highway 47 Kiske Junction near Mosul.[114]

Another country in the middle east, Syria, has used chlorine as a chemical weapon[115] delivered from barrel bombs and rockets.[116][117] In 2016, the OPCW-UN Joint Investigative Mechanism concluded that the Syrian government used chlorine as a chemical weapon in three separate attacks.[118] Later investigations from the OPCW's Investigation and Identification Team concluded that the Syrian Air Force was responsible for chlorine attacks in 2017 and 2018.[119]

Biological role

[edit]

The chloride anion is an essential nutrient for metabolism. Chlorine is needed for the production of hydrochloric acid in the stomach and in cellular pump functions.[120] The main dietary source is table salt, or sodium chloride. Overly low or high concentrations of chloride in the blood are examples of electrolyte disturbances. Hypochloremia (having too little chloride) rarely occurs in the absence of other abnormalities. It is sometimes associated with hypoventilation.[121] It can be associated with chronic respiratory acidosis.[122] Hyperchloremia (having too much chloride) usually does not produce symptoms. When symptoms do occur, they tend to resemble those of hypernatremia (having too much sodium). Reduction in blood chloride leads to cerebral dehydration; symptoms are most often caused by rapid rehydration which results in cerebral edema. Hyperchloremia can affect oxygen transport.[123]

Hazards

[edit]
Chlorine
Hazards
GHS labelling:[124]
GHS03: Oxidizing GHS06: Toxic GHS09: Environmental hazard
Danger
H270, H315, H319, H330, H335, H400
P220, P233, P244, P261, P304, P312, P340, P403, P410
NFPA 704 (fire diamond)

Chlorine is a toxic gas that attacks the respiratory system, eyes, and skin.[126] Because it is denser than air, it tends to accumulate at the bottom of poorly ventilated spaces. Chlorine gas is a strong oxidiser, which may react with flammable materials.[127][128]

Chlorine is detectable with measuring devices in concentrations as low as 0.2 parts per million (ppm), and by smell at 3 ppm. Coughing and vomiting may occur at 30 ppm and lung damage at 60 ppm. About 1000 ppm can be fatal after a few deep breaths of the gas.[18] The IDLH (immediately dangerous to life and health) concentration is 10 ppm.[129] Breathing lower concentrations can aggravate the respiratory system and exposure to the gas can irritate the eyes.[130] When chlorine is inhaled at concentrations greater than 30 ppm, it reacts with water within the lungs, producing hydrochloric acid (HCl) and hypochlorous acid (HOCl).

When used at specified levels for water disinfection, the reaction of chlorine with water is not a major concern for human health. Other materials present in the water may generate disinfection by-products that are associated with negative effects on human health.[131][132]

In the United States, the Occupational Safety and Health Administration (OSHA) has set the permissible exposure limit for elemental chlorine at 1 ppm, or 3 mg/m3. The National Institute for Occupational Safety and Health has designated a recommended exposure limit of 0.5 ppm over 15 minutes.[129]

In the home, accidents occur when hypochlorite bleach solutions come into contact with certain acidic drain-cleaners to produce chlorine gas.[133] Hypochlorite bleach (a popular laundry additive) combined with ammonia (another popular laundry additive) produces chloramines, another toxic group of chemicals.[134]

Chlorine-induced cracking in structural materials

[edit]
Chlorine "attack" on an acetal resin plumbing joint resulting from a fractured acetal joint in a water supply system which started at an injection molding defect in the joint and slowly grew until the part failed. The fracture surface shows iron and calcium salts that were deposited in the leaking joint from the water supply before failure and are the indirect result of the chlorine attack.

Chlorine is widely used for purifying water, especially potable water supplies and water used in swimming pools. Several catastrophic collapses of swimming pool ceilings have occurred from chlorine-induced stress corrosion cracking of stainless steel suspension rods.[135] Some polymers are also sensitive to attack, including acetal resin and polybutene. Both materials were used in hot and cold water domestic plumbing, and stress corrosion cracking caused widespread failures in the US in the 1980s and 1990s.[136]

Chlorine–iron fire

[edit]

The element iron can combine with chlorine at high temperatures in a strong exothermic reaction, creating a chlorine–iron fire.[137][138] Chlorine–iron fires are a risk in chemical process plants, where much of the pipework that carries chlorine gas is made of steel.[137][138]

See also

[edit]

Notes

[edit]

References

[edit]
[edit]
Revisions and contributorsEdit on WikipediaRead on Wikipedia
from Grokipedia
Chlorine is a with the symbol Cl and 17, classified as a in group 17 of the periodic table. It exists as a diatomic gas (Cl₂) at , exhibiting a distinctive pale yellow-green color and pungent odor due to its high reactivity. Discovered in 1774 by Swedish chemist through the reaction of with —initially mistaken for an oxygenated compound—chlorine was later identified as a distinct element in 1810 by , who derived its name from the Greek word chlôros meaning "greenish-yellow." Highly toxic as a pulmonary irritant, chlorine reacts vigorously with to form hydrochloric and hypochlorous acids, enabling its extensive industrial applications including water disinfection to eliminate pathogens, production of (PVC) plastics, and bleaching processes in pulp and textiles. In biological systems, the chloride ion (Cl⁻) serves essential roles as the primary extracellular anion, maintaining , electrical neutrality, and facilitating acid-base balance, nerve impulse transmission, and cellular volume regulation. Notably, chlorine's deployment as a chemical weapon by at the Second in 1915 marked the first large-scale use of poison gas in , releasing approximately 168 tons of the gas to asphyxiate and injure Allied troops via damage and in pulmonary fluids. Despite its hazards, chlorine's production exceeds 70 million tons annually, underscoring its indispensable yet double-edged role in chemistry and society.

Physical and Chemical Properties

Atomic Structure and Isotopes

Chlorine possesses an of 17, indicating a nucleus containing 17 protons and, in its neutral state, 17 electrons arranged around the nucleus. The of a chlorine atom is 1s² 2s² 2p⁶ 3s² 3p⁵, equivalent to [Ne] 3s² 3p⁵, with seven valence electrons in the 3p orbitals conferring high of 3.16 (Pauling scale) and reactivity typical of . Chlorine exhibits common oxidation states of −1 (as the chloride ion) and +1 to +7 in oxyanions and other compounds; its covalent atomic radius is 99 pm, and the first ionization energy is 12.97 eV. The nucleus includes neutrons whose number varies among isotopes, contributing to the element's variation while preserving chemical similarity due to identical s. Chlorine features two stable isotopes: chlorine-35 (³⁵Cl) and chlorine-37 (³⁷Cl). ³⁵Cl, comprising 17 protons and 18 neutrons, constitutes 75.77% of naturally occurring chlorine, while ³⁷Cl, with 17 protons and 20 neutrons, accounts for 24.23%. These abundances yield an average of 35.453 u. Radioactive isotopes exist, such as chlorine-36 (³⁶Cl), produced cosmogenically with a of approximately 301,000 years, but occur in trace amounts negligible for bulk elemental properties.
IsotopeAtomic Mass (u)Natural Abundance (%)Neutron Count
³⁵Cl34.9688575.7718
³⁷Cl36.9659024.2320
This isotopic distribution influences applications like , where chlorine's characteristic M+2 peak arises from the ~3:1 of ³⁵Cl to ³⁷Cl.

Physical Characteristics

Chlorine exists as a diatomic molecule (Cl₂) and is a gas at standard temperature and pressure, exhibiting a characteristic greenish-yellow color and a pungent, irritating odor detectable at concentrations as low as 0.2 parts per million. The gas is denser than air, with a vapor density of approximately 2.5 relative to air and an absolute density of 3.2 g/L at 0°C and 1 atm. This density causes it to accumulate in low-lying areas, contributing to its hazards in confined spaces. The element transitions to a state under moderate or cooling, appearing as a clear amber-colored with a of 1.4085 g/mL at -35°C. Its is -101.5°C, and the is -34.04°C at 1 , allowing at under pressures around 6-7 .
PropertyValue
Molar mass
Density (gas, STP)
Density (liquid, -35°C)
Melting point
Boiling point
Solubility in water (20°C)
Chlorine demonstrates limited in , approximately 0.3% to 0.7% by weight depending on , decreasing with rising due to its exothermic dissolution. It is non-flammable but supports of other materials as a strong oxidizer. In form, chlorine forms orthorhombic crystals, though it is rarely handled as a solid due to its low .

Reactivity and Thermodynamic Properties

Chlorine (Cl₂) is a potent , with a standard of 1.396 V for the Cl₂(g) + 2e⁻ → 2Cl⁻(aq), reflecting its strong thermodynamic drive to accept electrons and oxidize other substances under standard conditions. This property underpins its reactivity with a broad array of elements and compounds, excluding , where it typically displaces less electronegative from their compounds via exothermic halide exchange reactions. The Cl–Cl single bond dissociation energy of 242.6 kJ/mol facilitates bond cleavage, enabling rapid reactions, though it is stronger than the F–F bond due to reduced lone-pair repulsion. With , chlorine reacts explosively upon initiation by light, heat, or catalysts to form : H₂(g) + Cl₂(g) → 2HCl(g), a highly driven by the formation of strong H–Cl bonds (bond energy approximately 431 kJ/mol each) exceeding the energies of the reactant bonds (H–H at 436 kJ/mol and Cl–Cl at 243 kJ/mol). This reaction occurs over a wide concentration range (4–93% ) and exemplifies chlorine's role in chain reactions propagated by Cl• radicals. With most metals, chlorine undergoes vigorous, often incandescent reactions to yield metal chlorides, such as 2Na(s) + Cl₂(g) → 2NaCl(s), which are thermodynamically favored by the high lattice energies of ionic chlorides and negative enthalpies of formation (e.g., ΔH_f° for NaCl(s) = –411 kJ/mol). In , chlorine partially disproportionates to and : Cl₂(g) + H₂O(l) ⇌ HOCl(aq) + HCl(aq), with an K ≈ 3.9 × 10⁻⁴ at 25°C, favoring reactants but enabling bleaching and disinfection via formation under neutral to basic conditions. Chlorine also reacts with many non-metals and organics, supporting akin to oxygen and igniting materials like at low temperatures (e.g., 50°C for dry ). Key thermodynamic parameters for Cl₂(g) at 298 and 1 bar include a S° of 223.08 J/mol·K and a constant-pressure C_p° of approximately 33.0 J/mol·K (from Shomate equation fits). As the , its and of formation are zero by convention (ΔH_f° = 0 kJ/mol, ΔG_f° = 0 kJ/mol), providing the for assessing reaction spontaneity in chlorine-involved processes.

Natural Occurrence

Abundance in Earth's Crust and Oceans

Chlorine constitutes approximately 145 parts per million (ppm) by mass in the Earth's crust, ranking it among the less abundant elements despite its presence in various chloride minerals such as halite (NaCl) and sylvite (KCl). This low crustal concentration reflects chlorine's high solubility in aqueous environments, which preferentially partitions it into surface waters and sedimentary deposits rather than silicate rocks. Estimates vary slightly, with some geochemical analyses placing it at 170–180 ppm, but standardized compilations converge on 145 ppm as a representative value derived from averaged rock analyses. In contrast, the oceans represent the dominant reservoir of chlorine on , primarily as dissolved ions (Cl⁻), which account for over half of seawater's total . typically contains 18,980–19,400 mg/L of , with a standard average of about 19,000 mg/L, making Cl⁻ the most abundant anion by equivalents. This concentration arises from long-term leaching of crustal chlorides by hydrological cycles, with minimal due to chlorine's conservative behavior in marine systems—its distribution remains uniform across ocean basins, varying primarily with gradients from or freshwater influx. The total chlorine mass in the oceans is estimated at 2.6 × 10¹⁶ metric tons, vastly exceeding crustal reserves due to the hydrosphere's volume of roughly 1.4 × 10²¹ liters. This oceanic predominance underscores chlorine's geochemical mobility, with evaporite deposits (e.g., salt domes) forming secondary crustal concentrations through cyclic precipitation in marginal seas.

Geochemical Distribution

Chlorine is predominantly distributed in Earth's surface reservoirs as chloride ions (Cl⁻), with the oceans serving as the largest accessible geochemical sink, containing approximately 546 mmol/kg of dissolved chlorine, equivalent to about 1.94% by weight. This concentration arises from long-term mantle , which has transferred roughly 40% of the planet's total chlorine inventory to the crust and over geological time. In contrast, the mantle retains the bulk of Earth's chlorine due to its vast volume, despite lower concentrations. In the continental crust, chlorine averages 180 ppm, primarily hosted in evaporite minerals such as (NaCl), (KCl), and (KMgCl₃·6H₂O), which form through in arid basins. Sedimentary rocks, particularly salt domes and bedded s, concentrate chlorine far above crustal averages, with deposits like those in the Permian Zechstein Basin or representing significant long-term sinks derived from ancient marine brines. Igneous and metamorphic rocks contain lower levels, typically 10–50 ppm, incorporated into accessory minerals like (Ca₅(PO₄)₃Cl), , and amphiboles, or as inclusions in fluids and grain boundaries. The holds about 100 ppm chlorine, largely incompatible and partitioned into fluids during , with evidence from mantle xenoliths and ocean island basalts indicating recycling via subducted oceanic lithosphere enriched by alteration. exhibits elevated chlorine (up to several hundred ppm) in altered basalts and sediments due to hydrothermal exchange with , facilitating subduction-zone transfer back to . Atmospheric and pedospheric chlorine is negligible, with sea-salt aerosols and minor volcanic HCl contributing transiently before deposition into soils or oceans.
ReservoirApproximate Chlorine ConcentrationPrimary Form/Host
19,000 ppm (1.94 wt%)Dissolved Cl⁻ ions
180 ppmEvaporites (e.g., ), accessory silicates
100 ppmFluid inclusions, nominally anhydrous minerals
Oceanic Crust (altered)100–500 ppmHydrothermally altered basalts, pore fluids

History

Discovery and Early Observations

Chlorine was first isolated in 1774 by Swedish chemist through the reaction of with pyrolusite (). heated a of these substances, producing a greenish-yellow gas that he described as having a suffocating and powerful bleaching properties. He observed that the gas reacted with metals to form corrosive products and, when combined with solutions, yielded common salt, indicating its for sodium. At the time, did not recognize the gas as a distinct element, instead viewing it within the as a compound related to "muriatic acid" (). Early experiments revealed chlorine's reactivity and . Scheele noted its ability to decompose organic materials and its irritating effects on the , though systematic toxicity studies were absent. French chemist later applied chlorine's bleaching action in processing around 1785, confirming its decolorizing power on dyes through oxidation rather than simple absorption. These observations highlighted chlorine's oxidizing , as it readily accepted electrons from other substances, a property rooted in its high . In 1810, British chemist definitively established chlorine as an element by decomposing various "muriates" (chlorides) and failing to break it further, naming it from "chloros," meaning greenish-yellow, to reflect its distinctive color. Davy's electrochemical experiments demonstrated that chlorine could not be reduced to simpler gaseous components, distinguishing it from compounds and aligning with emerging atomic theory. This recognition shifted understanding from a hypothetical oxide of muriatic acid to a fundamental element.

Isolation and Characterization

Chlorine gas was first isolated in 1774 by Swedish chemist through the reaction of manganese(IV) oxide (pyrolusite) with , yielding a greenish-yellow gas that he described as having a suffocating odor and bleaching properties. Scheele believed this substance to be a compound of with oxygen, terming it "dephlogisticated muriatic acid," consistent with the prevalent at the time. In 1810, British chemist Humphry Davy recognized chlorine as a distinct element after conducting electrolysis experiments on muriatic acid (aqueous HCl) and related compounds, demonstrating that the gas could not be further decomposed and lacked oxygen, contrary to earlier assumptions. Davy named the element "chlorine" from the Greek word khloros, meaning greenish-yellow, reflecting its distinctive color. He characterized it as a highly reactive gas that forms acids with hydrogen, bleaches organic materials through oxidative decomposition rather than oxygenation, and combines vigorously with most elements except noble gases and inert substances. Early characterization efforts by Davy and contemporaries established chlorine's physical properties, including its boiling point of approximately -34°C, density about 2.5 times that of air, and solubility in water to form hydrochloric and hypochlorous acids. Chemical analyses confirmed its diatomic nature (Cl₂) and position as a halogen, with reactivity decreasing down the group, though precise atomic weight determination awaited later spectroscopic and electrochemical methods in the 19th century. These findings solidified chlorine's elemental status, distinguishing it from compounds like oxymuriatic acid hypothesized by French chemists.

Industrial and Scientific Milestones

In 1799, Scottish chemist patented a process for manufacturing bleaching powder by reacting chlorine gas with dry slaked lime to form , enabling efficient dry bleaching for textiles and marking the onset of large-scale chlorine utilization.) scaled production rapidly, reaching over 100 tons annually by the 1820s and becoming a cornerstone of the emerging , though reliant on small-scale chlorine generation from HCl and MnO2. Mid-19th-century innovations addressed HCl byproducts from the Leblanc soda ash process, enabling chlorine recovery. The Weldon process, developed by Walter Weldon around 1866–1870, reacted HCl with to produce chlorine while regenerating manganese via lime treatment, reducing waste but requiring significant fuel. In 1868, Henry Deacon advanced this with the catalytic process, oxidizing HCl with air over cupric chloride at 400–450°C, yielding up to 80% chlorine conversion and facilitating direct gas production for industrial applications. Electrolytic methods transformed production in the late by directly decomposing . The Castner-Kellner , introduced in 1890, used mercury cathodes to form from NaCl , liberating chlorine at the and enabling coupled caustic soda output without HCl waste. This mercury cell approach gained prominence, with the first U.S. commercial electrolytic chlorine facility starting operations in Rumford Falls, , in 1892 for production. By 1924, North American chlorine capacity reached approximately 180,000 tons annually, underscoring the shift to efficient, scalable .

Production

Chloralkali Electrolysis Processes

The chloralkali process is the primary industrial method for producing chlorine gas through the electrolysis of aqueous sodium chloride (brine), yielding chlorine at the anode, hydrogen gas at the cathode, and sodium hydroxide as a byproduct. The overall reaction is 2NaCl + 2H₂O → Cl₂ + H₂ + 2NaOH, with anodic oxidation of chloride ions (2Cl⁻ → Cl₂ + 2e⁻) and cathodic reduction of water (2H₂O + 2e⁻ → H₂ + 2OH⁻), as sodium ions migrate to maintain charge balance. This electrolytic decomposition requires direct current and operates in specialized cells to separate products and prevent recombination. Historically, the process traces to early 19th-century experiments, with William Cruikshank demonstrating brine for chlorine in 1800, though industrial-scale implementation began in the using dynamic cells and later electrolytic cells patented in the . Three main cell technologies have dominated: mercury cells, diaphragm cells, and cells, each differing in design, product separation, and environmental impact. Mercury cells, introduced in the late , use a mercury to form a , which is then decomposed to produce pure , but require higher voltage (around 4.5 V) and have been largely phased out globally since the due to mercury emissions contaminating waterways and bioaccumulating in , as evidenced by elevated mercury levels in effluents exceeding safe thresholds. Diaphragm cells, employing an or diaphragm to separate and compartments, operate at lower voltages (about 3.5 V) with less pure feedstock but produce contaminated with , necessitating further purification, and face restrictions due to health risks. Membrane cells, developed in the 1970s with ion-exchange membranes selective for sodium ions, now predominate, offering higher energy efficiency, purer sodium hydroxide (typically 32-35% concentration with low salt content), and no mercury or asbestos use, though requiring ultrapure brine to avoid membrane fouling. These cells achieve current efficiencies over 95% and voltage drops around 3-3.5 V, reducing electricity consumption to about 2,200-2,500 kWh per ton of chlorine compared to 3,200-3,500 kWh for older technologies. Approximately 95% of global chlorine production, exceeding 70 million metric tons annually as of recent estimates, relies on chloralkali electrolysis, with membrane technology comprising over 80% of capacity in regions like Europe and North America.

Alternative Production Methods and Innovations

The Deacon process represents a key alternative to chloralkali for chlorine production, particularly for recycling byproduct from organic chlorination reactions in the . Developed in 1868 by Henry Deacon, it involves the of HCl gas with atmospheric oxygen: 4HCl + O₂ → 2Cl₂ + 2H₂O, typically conducted at 400–450°C using cupric chloride (CuCl₂) as the initial catalyst, which undergoes cyclic oxidation and chlorination. This method achieves equilibrium-limited conversions of around 60–70% per pass due to the reaction's exothermicity and reversibility, necessitating multiple stages or product separation for viability, and it has been applied industrially to recover up to 10–15% of total chlorine output in integrated facilities. Modern innovations in the Deacon process have addressed catalyst deactivation from formation and by employing (RuO₂)-based catalysts, introduced commercially around 2004, which enable operations at lower temperatures (300–400°C) with improved selectivity exceeding 90% and longer catalyst lifetimes. These catalysts operate via a Mars-van Krevelen mechanism involving HCl dissociation, chlorine desorption, and oxygen on the surface, reducing demands compared to classical variants. Further advancements include systems, such as KCl-CuCl₂ electrolytes, which facilitate HCl oxidation at moderate temperatures with oxychloride intermediates, offering potential for higher efficiency in niche applications like byproduct recovery from HCl-rich streams. Emerging electrochemical alternatives to direct HCl oxidation have been explored for sustainable chlorine generation, bypassing oxygen's limitations in gas-phase processes, though they remain non-commercial at scale as of 2025. These include anode-driven Cl⁻ oxidation in divided cells, achieving near-theoretical yields but requiring pure HCl feeds and facing challenges from melts. Overall, while chloralkali accounts for over 95% of global , Deacon-derived methods provide economically viable recycling pathways, with innovations focusing on catalyst durability and integration with renewable sources to mitigate CO₂ emissions from oxygen compression and heating.

Chemistry and Compounds

Binary Chlorides and Hydrogen Chloride

(HCl) is a diatomic covalent formed by the bonding of and chlorine atoms. It exists as a colorless gas at standard conditions, exhibiting a sharp, pungent detectable at concentrations as low as 0.5 parts per million. Its molecular weight is 36.461 g/mol, with a of -85.05 °C and a of -114.22 °C. When dissolved in , HCl ionizes completely to form ions and ions, yielding , a strong monoprotic acid with pKa ≈ -6.3 that reacts vigorously with metals, bases, and oxides. Hydrogen chloride is prepared industrially primarily through the direct, exothermic combination of hydrogen and chlorine gases: H₂ + Cl₂ → 2HCl, often catalyzed and controlled to manage the reaction's intensity. An alternative laboratory or smaller-scale method involves heating sodium chloride with concentrated sulfuric acid: NaCl + H₂SO₄ → NaHSO₄ + HCl (at lower temperatures), followed by further heating to Na₂SO₄ + 2HCl for higher yields. The gas is highly soluble in water (up to 720 volumes per volume at 20 °C), but its solubility decreases with rising temperature, leading to evolution of HCl gas upon heating concentrated solutions. In reactions, HCl acts as a source of chloride ions and protons, forming salts with metals (e.g., Zn + 2HCl → ZnCl₂ + H₂) and participating in hydrolysis or fuming behaviors in moist air due to affinity for water. Binary chlorides comprise compounds of chlorine with a single other element, typically exhibiting ionic character with electropositive metals or covalent character with elements of comparable . Ionic binary chlorides, such as those of and alkaline earth metals (e.g., NaCl, MgCl₂), feature lattice structures stabilized by electrostatic attractions between cations and Cl⁻ anions, resulting in high melting points (e.g., NaCl at 801 °C) and solubility in polar solvents like , where they dissociate into ions. These are commonly prepared by neutralizing metal oxides or hydroxides with HCl or by direct combination of the metal with chlorine gas. Covalent binary chlorides predominate among p-block elements, displaying molecular structures, volatility, and often hydrolytic due to weaker intermolecular forces and polar Cl-E bonds prone to nucleophilic attack by . Examples include (PCl₃, boiling point 76 °C), (PCl₅, sublimes at 160 °C), (SiCl₄, boiling point 57 °C), and sulfur dichloride (SCl₂, boiling point 59 °C), prepared via direct chlorination (e.g., 2P + 3Cl₂ → 2PCl₃ or P₄ + 10Cl₂ → 4PCl₅). These compounds transition from ionic to covalent bonding across period 3 elements, with aluminum chloride (AlCl₃) bridging as a dimeric (Al₂Cl₆) that sublimes at 180 °C and hydrolyzes exothermically. chlorides, like FeCl₃ or TiCl₄, often show mixed ionic-covalent traits, with TiCl₄ being a volatile liquid (boiling point 136 °C) used in synthesis due to its Lewis acidity. Overall, binary chlorides' properties reflect differences and coordination geometries, influencing their roles as chlorinating agents or intermediates in inorganic synthesis.

Interhalogen and Polychlorine Compounds

Interhalogen compounds consist of two or more atoms of different elements bonded covalently, with the less electronegative typically serving as the central atom. Chlorine participates in several such compounds, most notably with , , and iodine, due to the expanded octet capability of chlorine allowing coordination numbers up to five or seven in some cases. These compounds are generally more reactive than the parent , exhibiting strong oxidizing properties and tendency to disproportionate or react vigorously with , organic materials, and metals. Chlorine fluorides represent the most stable and well-characterized interhalogens involving chlorine. (ClF) is synthesized by direct combination of chlorine and gases in a 1:1 ratio at approximately 300 °C, yielding a pale yellow gas with a of -100 °C and of -156 °C. It adopts a linear structure and serves as a fluorinating agent in , though its high reactivity limits handling to specialized equipment. (ClF₃), prepared by reacting excess with chlorine or ClF at elevated temperatures around 300 °C, is a colorless gas that liquefies at 11 °C and solidifies at -76 °C; its T-shaped arises from a trigonal bipyramidal arrangement with two lone pairs on chlorine. ClF₃ is notoriously reactive, igniting hydrocarbons, , and on contact, and has been employed as a oxidizer and in for . (ClF₅), formed similarly with further excess at 350–400 °C, exists as a colorless gas or pale yellow liquid ( 12 °C), featuring a square pyramidal structure; it acts as a powerful fluorinator but decomposes explosively under certain conditions. Chlorine also forms interhalogens with bromine and iodine, though these are less thermally stable than the fluorides. (BrCl) results from the equilibrium reaction of and chlorine gases, producing a deep gas that decomposes above 10 °C into the elements; it possesses a linear and functions as a brominating and chlorinating agent in . (ICl), obtained by reacting solid iodine with gaseous chlorine, appears as black needles or a ( 27 °C, 97 °C) and exhibits a linear ; it is used in iodometric titrations and as a catalyst in due to its moderate stability compared to other iodine chlorides. (ICl₃), often existing in equilibrium with ICl and Cl₂ or as the dimeric [ICl₂]⁺[ICl₄]⁻ in solid state, adopts a planar in the and serves in processes, though it hydrolyzes readily in moist air. Polychlorine compounds, encompassing species with multiple chlorine atoms bonded together beyond the diatomic Cl₂, are rare and unstable in neutral form due to weak Cl-Cl bond strengths (approximately 243 kJ/mol) and repulsion in higher coordination. Neutral trichlorine (Cl₃) has been transiently observed in gas-phase spectroscopic studies but lacks isolable character. More stable polychlorine entities appear in ionic polyhalide forms, such as the trichloride anion Cl₃⁻, which forms weakly in solutions of chloride salts with Cl₂ in non-aqueous solvents like and exhibits a bent structure with Cl-Cl bond lengths around 2.0 ; however, it decomposes readily to Cl⁻ and Cl₂. Mixed polyhalides incorporating chlorine, such as [ICl₂]⁻ (linear, with iodine central) and [BrCl₂]⁻, occur in salts like tetraalkylammonium or derivatives and arise from addition of Cl₂ to ICl or BrCl, displaying greater stability in solid state but hydrolyzing in water to and ions. These polyhalides serve as intermediates in halogen exchange reactions and highlight chlorine's limited propensity for compared to or carbon.

Oxides, Oxoacids, and Oxyanions

Chlorine forms several binary oxides, including (Cl₂O), (ClO₂), dichlorine trioxide (Cl₂O₃), (Cl₂O₆), and (Cl₂O₇), in which chlorine exhibits oxidation states from +1 to +7. These compounds are generally unstable, endothermic, and potent oxidizers, with tendencies to decompose explosively or react vigorously with and organics; for instance, Cl₂O hydrolyzes to and , while ClO₂, a yellow-green gas with a of 11 °C, detonates above 300 °C or in concentrated solutions due to its radical nature. Cl₂O₇, an oily liquid at , serves as the anhydride of and reacts with to form two equivalents of HClO₄. The oxoacids of chlorine derive from these oxides via and include (HClO, +1 state), (HClO₂, +3), (HClO₃, +5), and (HClO₄, +7). Stability and acid strength increase with higher oxidation states: HClO is a weak acid (pKₐ ≈ 7.5) that decomposes readily to Cl₂ and O₂, functioning primarily in aqueous solutions as an oxidant in disinfection processes. HClO₃, a colorless , is a strong acid that accelerates and corrodes metals, prepared by dissolving ClO₂ in hot water or via of solutions. HClO₄, among the strongest mineral acids (pKₐ ≈ -10), is a colorless fuming at concentrations above 70% that acts as a powerful hot oxidizer, capable of igniting organics, though dilute solutions are stable. The conjugate bases of these oxoacids form oxyanions: (ClO⁻), (ClO₂⁻), (ClO₃⁻), and (ClO₄⁻). These tetrahedral anions feature chlorine bonded to oxygen atoms, with exhibiting the highest stability due to delocalized charge; solutions (ca. 5-15% available chlorine) disproportionate over time to and , while are inert under ambient conditions but form mixtures when dry with combustibles. and serve in and propulsion, with providing 250-300 seconds in solid rocket fuels.
OxoacidFormulaOxidation State of ClKey Properties
Hypochlorous acidHClO+1Weak acid; unstable; primary oxidant in bleach solutions
Chlorous acidHClO₂+3Unstable; decomposes to ClO₂ and HClO
Chloric acidHClO₃+5Strong acid; ignites combustibles; corrosive
Perchloric acidHClO₄+7Superacid; strong hot oxidizer; used in analysis

Organochlorine Compounds

Organochlorine compounds are synthetic organic molecules featuring at least one carbon-chlorine bond, encompassing a diverse array of structures including chlorinated alkanes, alkenes, aromatics, and polymers. These compounds typically exhibit high , low , high , and resistance to , properties that facilitate their persistence in the environment and in fatty tissues of organisms. Synthesis generally involves free-radical chlorination of hydrocarbons, addition of chlorine or to unsaturated bonds, or substitution reactions, often yielding mixtures requiring purification. Prominent examples include simple chlorinated solvents such as (CHCl₃) and (CCl₄), historically employed for degreasing, extraction, and as refrigerants due to their non-flammability and solvent efficacy. , produced via chlorination of or acetone, served in and until its hepatotoxic and carcinogenic effects—evidenced by and liver damage in acute exposures—prompted restrictions. , derived from chlorination, was widely used in and fire extinguishers but phased out after 1970s findings linked it to hepatotoxicity, , and probable human carcinogenicity via P450-mediated metabolism to toxic radicals. Both compounds' volatility and soil persistence contributed to contamination, with half-lives exceeding decades in anaerobic conditions. Organochlorine pesticides, such as (dichlorodiphenyltrichloroethane), exemplified agricultural applications post-World War II, dramatically reducing vector-borne diseases like and boosting crop yields through insecticidal action via nerve sodium channel disruption. However, their enabled in food chains, correlating with empirical observations of thinning in raptors and endocrine disruption in aquatic species, prompting bans in many nations by the 1970s-1980s under frameworks like the Stockholm Convention, which classifies most as persistent organic pollutants (POPs). Legacy residues persist in sediments and biota, with studies detecting DDT metabolites in remote samples due to atmospheric transport, though post-ban declines in concentrations affirm regulatory efficacy. Polymers like (PVC) represent high-volume organochlorines, formed by free-radical of monomer—itself produced by oxychlorination of with chlorine gas—at approximately 80% via suspension methods yielding resins for , , and devices. Global production exceeds 40 million metric tons annually, valued for PVC's toughness, abrasion resistance, flame retardancy, and resistance to acids and bases, though plasticizers and stabilizers are added to mitigate . During production or degradation, trace release poses carcinogenic risks, but engineered PVC formulations minimize such emissions compared to unregulated historical uses. Overall, while organochlorines' utility in industry and drove economic gains, their environmental tenacity—evident in long-range and trophic magnification—necessitated risk-based phase-outs for volatile and bioaccumulative subtypes, shifting reliance to less persistent alternatives where feasible.

Applications

Disinfection, Sanitation, and

Chlorine compounds, particularly solutions and chlorine gas, serve as primary disinfectants in municipal water supplies, , and recreational water systems by inactivating pathogenic microorganisms through oxidation. The process begins with chlorine dissolving in water to form (HOCl), the predominant active species at typical pH levels of 7.2–7.8, which penetrates microbial cell walls and oxidizes essential cellular components such as proteins, enzymes, and nucleic acids, leading to rapid inactivation. This mechanism achieves log reductions in bacteria like and viruses within minutes at residual concentrations of 0.2–1.0 mg/L, far surpassing alternatives like boiling in cost and scalability for large populations. The adoption of chlorination marked a pivotal advancement in public sanitation, with the first experimental municipal application in , , in 1897 using to treat contaminated , followed by permanent implementation in , in 1905 amid a typhoid . , , initiated continuous chlorination on February 26, 1908, under engineers George W. Fuller and physician John L. Leal, reducing typhoid fever cases from over 1,000 annually to near zero within years by treating the Boonton Reservoir supply. By 1914, over 100 U.S. cities had adopted the practice, correlating with a 90% decline in typhoid mortality rates from 36 per 100,000 in 1900 to under 4 per 100,000 by 1920. In and wastewater systems, chlorine residuals maintain disinfection throughout distribution networks, preventing regrowth of pathogens like Vibrio cholerae and Salmonella typhi, which historically caused millions of deaths; modern chlorination has virtually eradicated and typhoid in treated systems, averting an estimated 6–11% of under-five in high-burden areas per intervention studies. For recreational , chlorine at 1–3 mg/L in swimming pools oxidizes contaminants from swimmers, including fecal matter and sweat, reducing outbreaks of and E. coli infections by over 95% compared to untreated water, as evidenced by CDC surveillance data. Household bleach, a 5–6% sodium hypochlorite solution derived from chlorine, extends sanitation to surfaces and laundry; its disinfectant efficacy was recognized in 1847 for medical use in and has since proven effective against 99.9% of , viruses, and fungi at dilutions of 1:10–1:100, including robust pathogens like difficile spores within 10 minutes. Overall, these applications have transformed by curtailing waterborne disease transmission, with chlorination credited for saving billions of lives globally since 1900 through scalable, residual protection unmatched by filtration alone.

Industrial Chemical Synthesis

Chlorine serves as a primary feedstock in the industrial synthesis of organochlorine compounds, particularly through direct chlorination reactions that introduce chlorine atoms into hydrocarbons or other precursors. Approximately 40% of global chlorine production is directed toward polyvinyl chloride (PVC) manufacture via the vinyl chloride pathway. The process initiates with the exothermic addition of chlorine to ethylene, yielding 1,2-dichloroethane (C2H4 + Cl2 → ClCH2CH2Cl), typically conducted at 50–100°C under light or catalyst initiation to control radical chain reactions. This intermediate undergoes oxychlorination or thermal dehydrochlorination at 400–500°C to produce vinyl chloride monomer (CH2=CHCl) and regenerate hydrogen chloride, which is recycled in balanced processes to minimize waste. The vinyl chloride is then free-radical polymerized to form PVC resin, a versatile thermoplastic used in pipes, films, and coatings. Phosgene (COCl2) synthesis represents another major chlorine-consuming reaction, involving the catalytic combination of and chlorine gas (CO + Cl2 → COCl2) over at 50–150°C, achieving near-quantitative yields in continuous flow reactors. Global output exceeds 12 million tonnes annually, primarily as an intermediate for (TDI) and (MDI), which are hydrolyzed or reacted further into polyurethanes for foams, coatings, and elastomers. Hydrogen chloride byproduct from downstream phosgenation steps (e.g., with amines) is often neutralized or recycled, though demands inert handling due to 's high reactivity and . Chlorine also facilitates the production of chlorinated solvents and intermediates, such as (CHCl3) via photochlorination (CH4 + 3Cl2 → CHCl3 + 3HCl) or (CCl4) from and chlorine, though volumes have declined sharply since the 1990s phaseout for ozone-depleting substances. In pharmaceutical synthesis, chlorine enables selective chlorination of aromatic rings or side chains, as in the production of intermediates for antibiotics like or herbicides, leveraging under controlled conditions to enhance molecular potency without excessive byproducts. These processes underscore chlorine's role in enabling diverse and chains, with recycling of HCl often integrated to improve .

Other Commercial and Technical Uses

Chlorine is employed in the chloride for producing pigment, where or synthetic is reacted with chlorine gas and carbon at high temperatures (approximately 900–1000°C) to form volatile (TiCl4), which is then oxidized to TiO2 and purified, with chlorine recycled. This method accounts for a significant portion of global TiO2 production, offering advantages in purity and efficiency over processes, though it requires handling corrosive intermediates. Similarly, in titanium metal production via the Kroll , TiCl4—derived from chlorination of titanium ore—is reduced with magnesium, enabling the manufacture of lightweight alloys critical for and medical applications. In the , chlorine gas is used to treat fibers for shrink resistance, a process that partially degrades the scale structure on wool cuticles, reducing felting during washing; this is often followed by application of resins like Hercosett for enhanced durability. The chlorination step typically involves exposing wool to dilute chlorine solutions (0.5–2% available chlorine) under controlled and temperature, improving machine-washability of wool garments while minimizing damage to fiber strength. Despite environmental concerns over effluent adsorbable organic , this method remains a standard commercial approach due to its cost-effectiveness compared to enzymatic or plasma alternatives. Chlorinated paraffins, produced by direct chlorination of n-alkanes, serve as extreme-pressure additives in fluids, enhancing lubrication under high loads by forming protective chlorides on metal surfaces. They are also incorporated as secondary plasticizers and flame retardants in flexible PVC, rubber, paints, and sealants, where their high chlorine content (30–70%) imparts fire resistance and flexibility; short-chain variants (C10–13) were historically dominant but restricted in some regions due to persistence. Medium- and long-chain paraffins continue in these roles, supporting applications in cables, conveyor belts, and adhesives. In semiconductor fabrication, chlorine-based plasmas are utilized for anisotropic etching of silicon, III-V compounds, and metals in systems, where Cl2 dissociation generates reactive chlorine atoms and ions that selectively remove material via chemical and physical mechanisms. Etch rates can reach 1000–2000 Å/min for in inductively coupled plasmas with Cl2/BCl3 mixtures, enabling precise patterning for transistors and optoelectronic devices, though endpoint detection and passivation control are critical to avoid undercutting. This technical application supports advanced node fabrication, with chlorine's volatility aiding residue-free processes.

Biological Role

Chloride Ion in Physiology

The chloride ion (Cl⁻) is the principal anion in human , with a concentration of approximately 155 mM, accounting for about 66% of total extracellular anions. It maintains electroneutrality by counterbalancing cations such as sodium, contributes to regulation, and supports and acid-base balance across body compartments. Normal serum chloride levels range from 98 to 107 mEq/L, reflecting its abundance in plasma and . In gastric physiology, chloride ions are actively transported by parietal cells in the lining to pair with protons, forming (HCl) at concentrations up to 160 mM, which is vital for protein digestion, pathogen inactivation, and nutrient absorption. This depends on chloride conductance via channels like CFTR and is inhibited in the absence of extracellular Cl⁻, halting acid secretion. Chloride plays a key role in neuronal excitability through ionotropic GABA_A receptors, where GABA binding opens Cl⁻-permeable channels, typically allowing Cl⁻ influx that hyperpolarizes the membrane and inhibits firing, thus mediating fast synaptic inhibition. Intracellular Cl⁻ concentration, regulated by transporters like NKCC1 and KCC2, determines the reversal potential for currents, shifting from depolarizing in immature neurons to hyperpolarizing in mature ones. Disruptions in chloride manifest as (serum Cl⁻ <98 mEq/L), often from gastrointestinal losses like vomiting or renal wasting via diuretics, leading to metabolic alkalosis due to relative HCO₃⁻ excess, or hyperchloremia (>107 mEq/L), linked to , saline overload, or , promoting hyperchloremic . In , mutations in the CFTR gene encoding a cAMP-regulated Cl⁻ channel impair epithelial Cl⁻ , reducing airway surface liquid volume, impairing , and fostering chronic infections and in the lungs and other organs. This defect exemplifies chloride's critical transport function in secretory epithelia.

Absence of Elemental Chlorine Role

Elemental chlorine (Cl₂), the diatomic gas form of the element, has no established biological role in living organisms. Unlike the chloride ion (Cl⁻), which is incorporated into essential physiological processes such as balance, impulse transmission, and production, Cl₂ does not participate in any enzymatic reactions, structural biomolecules, or metabolic pathways. Its absence stems from inherent chemical instability in aqueous biological environments; Cl₂ rapidly hydrolyzes in water to form (HCl) and (HOCl), both of which are potent oxidants that disrupt cellular membranes, proteins, and DNA rather than supporting life functions. Although transient generation of chlorine-derived oxidants occurs in mammalian immune responses—such as the production of HOCl by to combat pathogens—no evidence indicates a functional incorporation of stable Cl₂ molecules into biological systems. Organisms lack mechanisms to synthesize, store, or utilize Cl₂ without inducing , as its high and oxidizing power (with the highest electron affinity among diatomic ) preclude safe integration into biochemistry. Exposure to Cl₂, even at low concentrations, causes acute respiratory irritation and tissue damage, underscoring its incompatibility with vital processes.

Toxicity and Health Effects

Acute Exposure Mechanisms

Chlorine gas primarily exerts acute toxic effects through inhalation, as it is denser than air and tends to accumulate in low-lying areas, facilitating rapid absorption via the respiratory tract. Upon contact with moist mucosal surfaces, chlorine (Cl₂) undergoes hydrolysis: Cl₂ + H₂O → HCl + HOCl, generating hydrochloric acid and hypochlorous acid, both of which are corrosive and contribute to immediate tissue irritation. Hypochlorous acid acts as a potent oxidant, reacting with cellular components such as amino acids, proteins, and lipids in the epithelial lining of the airways, leading to denaturation and sloughing of cells. This initial chemical injury triggers an inflammatory cascade, releasing cytokines and that recruit neutrophils and macrophages, exacerbating damage through and activity. In the upper airways, low concentrations (under 5 ppm) cause sensory , lacrimation, and due to stimulation of endings, while higher levels (above 15 ppm) induce via vagal reflexes and direct smooth muscle effects. In the lower respiratory tract, the intermediate water solubility of chlorine allows penetration to alveoli, where it disrupts function and increases , culminating in non-cardiogenic characterized by fluid accumulation and impaired . Severe exposures (e.g., 400 ppm for 30 minutes) can overwhelm compensatory mechanisms, resulting in (ARDS) through alveolar flooding, hypoxia, and potential asphyxiation. Ocular and dermal exposure to chlorine gas or liquid causes similar acid-mediated burns, with conjunctival and corneal ulceration from HOCl penetration into corneal stroma. These mechanisms underscore chlorine's role as a direct-acting irritant rather than a systemic , with effects proportional to concentration, duration, and particle size of any aerosolized form.

Chronic Exposure and Byproducts

Chronic exposure to low levels of chlorine gas, typically below 1-3 ppm as encountered in occupational environments like chlor-alkali plants or facilities, primarily affects the , manifesting as persistent eye and throat irritation, cough, and reduced airflow. Workers with prolonged exposure have shown evidence of chronic bronchitis, , and patterns, with dental also reported due to the gas's acidity. Epidemiological studies of low-dose chronic indicate associations with exacerbated and hay fever, particularly in sensitized individuals, though causation is not firmly established and severe pulmonary alterations are rare absent higher acute episodes. In recreational settings such as indoor pools, chronic low-level exposure to chlorine-derived —formed by reaction with sweat, , and —correlates with respiratory symptoms including hypersecretion, , and diminished lung function among regular swimmers and lifeguards. A 2021 study on low-dose chlorine (around 0.4 ppm) demonstrated worsened and production in animal models, mirroring human observations of increased bronchial reactivity. These effects stem from chlorine's role as an oxidant damaging epithelial barriers, with vulnerable populations like children showing heightened sensitivity. Chlorine used in disinfection reacts with natural , , and nitrogenous compounds to produce disinfection byproducts (DBPs), including trihalomethanes (THMs) such as and haloacetic acids (HAAs) like , which constitute 50-75% of halogenated DBPs by weight. Formation occurs via chlorination of , with levels varying by source quality and treatment; typical THM concentrations range from 20-100 μg/L in chlorinated systems. Chronic ingestion of exceeding EPA maximum contaminant levels (80 μg/L for total THMs, 60 μg/L for HAA5) over decades has been linked in cohort studies to elevated risks of liver, , and issues, alongside potential odds ratios of 1.2-1.9 in high-exposure groups. Epidemiological evidence associates long-term DBP exposure with reproductive effects, such as and preterm delivery, and , attributed to genotoxic and cytotoxic mechanisms disrupting cellular repair. and dermal absorption during showering or amplify DBP uptake, with volatile THMs contributing to airway akin to direct chlorine effects. Regulatory frameworks, including the U.S. EPA's Stage 2 Disinfectants and Disinfection Byproducts Rule implemented in , mandate monitoring and treatment optimizations like enhanced to curb DBP formation while preserving microbial safety. Despite these measures, residual risks persist in source waters high in organics, prompting alternatives like chloramination, which reduces THMs but generates other nitrogenous DBPs.

Epidemiological Evidence on Risks vs. Benefits

Epidemiological studies demonstrate that widespread chlorination of drinking water has substantially reduced mortality from waterborne diseases. In U.S. cities adopting chlorination and filtration between 1900 and 1936, these interventions accounted for nearly half of the aggregate decline in total mortality, with a 43% overall reduction, including 74% drops in infant mortality and 67% in child mortality rates under age 10. Similarly, water filtration alone reduced typhoid fever deaths by an average of 46%, contributing to the near-eradication of the disease by 1936. In developing contexts, chlorination programs have lowered all-cause under-five mortality by 6-11%, primarily through prevention of diarrheal diseases. The U.S. Centers for Disease Control and Prevention (CDC) recognizes water chlorination as one of the 10 greatest public health achievements of the 20th century, crediting it with dramatic declines in cholera, typhoid, and other outbreaks following its adoption starting in 1908. Disinfection byproducts (DBPs) formed during chlorination, such as trihalomethanes (THMs), have been linked in cohort and case-control studies to modestly elevated risks of certain cancers. Meta-analyses indicate a relative risk of bladder cancer approximately 1.2-1.4 for long-term consumers of chlorinated water, with dose-dependent associations for THMs like chloroform and bromodichloromethane. Evidence for colorectal and endometrial cancers is weaker and inconsistent, with some studies showing no significant link after confounder adjustment. The International Agency for Research on Cancer classifies chlorinated drinking water as Group 3 (not classifiable as to carcinogenicity in humans) due to inadequate evidence of causation despite plausible toxicological mechanisms. Quantitative risk-benefit assessments consistently affirm that chlorination's benefits in averting infectious disease mortality far exceed DBP-related risks, particularly given the low absolute incidence of associated cancers (e.g., attributable fractions under 5% for in high-exposure populations). Regulatory bodies like the CDC and endorse chlorine at residuals up to 4 mg/L as safe and effective for microbial control, with DBP regulations (e.g., U.S. maximum contaminant levels for THMs at 80 μg/L) mitigating potential hazards without compromising disinfection efficacy. Historical counterfactuals suggest that forgoing chlorination would result in orders-of-magnitude higher mortality from pathogens like Vibrio cholerae and Salmonella typhi than any DBP-attributable effects.

Military and Weapon Applications

Chemical Warfare History

Chlorine was first deployed as a chemical weapon on a large scale during the Second Battle of Ypres on April 22, 1915, when German forces released approximately 168 tons of the gas from 5,730 cylinders positioned along a 6-kilometer front against Allied positions held primarily by French colonial troops and Canadian divisions. The greenish-yellow cloud, denser than air, drifted toward enemy lines under favorable wind conditions, causing severe respiratory irritation, pulmonary edema, and asphyxiation by reacting with lung moisture to form hydrochloric acid. This initial attack resulted in around 5,000 immediate deaths and over 10,000 casualties among unprepared troops lacking effective masks, though exact figures vary due to chaotic retreats and incomplete records. The deployment, overseen by chemist Fritz Haber, marked a tactical shift toward gas warfare to break the Western Front stalemate, exploiting chlorine's industrial availability and toxicity at concentrations as low as 400 ppm. German forces conducted subsequent chlorine releases in WWI, including at Wieltje on May 2, 1915, but efficacy diminished due to unpredictable winds dispersing gas back on their own lines and rapid Allied adoption of countermeasures like urine-soaked cloths and primitive masks. By late 1915, Allies retaliated with chlorine at Loos, releasing 140 tons but achieving limited success amid adverse weather, underscoring chlorine's logistical vulnerabilities compared to later agents like . Overall, chemical weapons, starting with chlorine, inflicted about 1.3 million casualties and 90,000 deaths across the war, though chlorine-specific fatalities declined as mixtures and irritants supplanted it. These attacks prompted international revulsion, contributing to the 1925 , signed on June 17 by 38 nations, which prohibited the use in war of "asphyxiating, poisonous or other gases" but lacked enforcement mechanisms or bans on production and stockpiling. Post-WWI applications of chlorine in warfare were sporadic and often improvised. During the 1980-1988 Iran- War, employed chlorine alongside mustard and agents in some attacks, though documentation emphasizes the latter's dominance; precise chlorine incidents remain less verified amid broader chemical campaigns causing tens of thousands of casualties. deployed chlorine in nearly 20 bombs between late 2006 and mid-2007 targeting security forces and civilians in Anbar Province, killing dozens and injuring hundreds through blast-dispersed gas, before disruptions halted such efforts. In the , chlorine was used in at least 14 confirmed or likely incidents by regime forces via helicopter-dropped barrel bombs, as determined by the OPCW Fact-Finding Mission through sample analysis, witness testimonies, and trajectory evidence; notable cases include attacks in Douma on April 7, 2018, killing 43 and injuring over 500 via toxic inhalation. The OPCW's Investigation and Identification Team attributed these to strikes, citing delivery methods inconsistent with opposition capabilities, though denied involvement and contested sample chains of custody. Such uses violated the 2013 destruction agreement under OPCW supervision, highlighting enforcement challenges despite the 1997 Chemical Weapons Convention's comprehensive prohibitions.

Modern Restrictions and Alternatives

The for the Prohibition of the Use in War of Asphyxiating, Poisonous or Other Gases, and of Bacteriological Methods of Warfare, signed on June 17, 1925, marked the first international treaty explicitly banning the wartime deployment of chlorine and similar choking agents, responding to their extensive use in , where chlorine caused over 1.3 million casualties. This protocol, ratified by over 140 states, prohibits such gases but does not address production or stockpiling, leading to limited enforcement until later frameworks. The (CWC), adopted in 1993 and entering into force on April 29, 1997, imposes comprehensive restrictions by prohibiting the development, production, acquisition, stockpiling, transfer, and use of chemical weapons, including chlorine when deployed as a toxicant for warfare purposes. Administered by the Organisation for the Prohibition of Chemical Weapons (OPCW), the treaty classifies chlorine not as a scheduled chemical for outright bans in civilian contexts but deems its intentional release as a weapon—via munitions or deliberate dispersal—a violation, with 193 states parties as of 2025. Despite these prohibitions, violations persist; OPCW investigations confirmed Syrian government forces used chlorine gas in attacks, such as the April 7, killing 43 civilians and injuring hundreds, and the March 24-25, 2017, Ltamenah strikes. Recent allegations include Sudanese military deployment of chlorine in 2025 conflicts, highlighting enforcement challenges in non-compliant states. Enforcement relies on OPCW verification regimes, including destruction of declared stockpiles—over 98% of global declared chemical weapons eliminated by 2023—and challenge inspections, though dual-use nature of (produced industrially at 70 million tons annually) complicates regulation. Violations trigger sanctions, referral to the UN Security Council, or military responses, as in the 2018 U.S.-led strikes on Syrian facilities post-Douma. In response to these bans, militaries have shifted from chlorine-like choking agents to precision conventional munitions, drones, and non-lethal incapacitants for area denial or crowd control, avoiding the indiscriminate effects and international stigma of chemical deployment. Historical alternatives included phosgene or other pulmonary irritants, but these too fall under CWC prohibitions; modern doctrines emphasize kinetic weapons or binary nerve agents (also banned) only in legacy contexts, with most states destroying stockpiles under OPCW oversight by 2023. Toxic industrial chemicals like hydrogen fluoride or ammonia have been considered for improvised threats but lack chlorine's dispersibility and face similar legal barriers when weaponized. Overall, treaty compliance has reduced reliance on gas-based warfare, favoring verifiable, attributable conventional alternatives.

Hazards and Environmental Considerations

Material Degradation and Reactivity Risks

Chlorine, a potent , reacts vigorously with a wide array of materials, leading to degradation through , embrittlement, or . In its dry gaseous or liquid form, chlorine exhibits relatively low corrosivity toward , allowing storage in such vessels under conditions. However, the presence of even trace moisture hydrolyzes chlorine to form (HCl) and (HOCl), which accelerate uniform , pitting, and crevice attack on metals, potentially reducing equipment lifespan from years to months. Stainless steels, such as types 304 and 316, offer improved resistance in dry chlorine but remain susceptible to stress corrosion cracking (SCC) in damp environments above 50°C, where chloride ions penetrate passive oxide layers, initiating cracks that propagate rapidly under tensile stress. Nickel alloys like Hastelloy C-276 provide superior performance in wet chlorine service due to their high molybdenum content, which inhibits pitting, though they are costlier and still degrade over prolonged exposure. Reactive metals such as titanium must be avoided entirely in dry chlorine, as they ignite explosively upon contact, forming titanium tetrachloride. Polymers and elastomers suffer oxidative degradation from chlorine, with materials like , , and Buna-N swelling, cracking, or dissolving due to chlorination of carbon-hydrogen bonds. Fluoropolymers such as PTFE (Teflon) exhibit excellent compatibility, resisting permeation and chemical attack, while PVC and degrade severely in concentrated chlorine solutions, releasing HCl and compromising structural integrity. These interactions heighten risks in , valves, and , where incompatibility has contributed to leaks; for instance, corrosion-induced failures in chlorine handling systems have led to over 40 major releases exceeding 1 ton since 1992, often exacerbated by moisture ingress. Reactivity risks extend to ignition hazards, as chlorine supports of organics and reduces agents, potentially forming mixtures or fires upon contact with contaminants like oils or . Industrial guidelines mandate thorough passivation of equipment to remove residues, with regular inspections to detect early degradation, underscoring that material selection must account for operational conditions to mitigate catastrophic failures.

Emission Controls and Byproduct Formation

Industrial facilities producing or handling chlorine gas, primarily through the chlor-alkali process, employ wet to capture and neutralize fugitive emissions of Cl₂ and HCl by reacting them with alkaline solutions such as , achieving removal efficiencies exceeding 99% in many systems. Ventilation systems with high air exchange rates, often changing room air every minute, combined with continuous monitoring via sensors, prevent accumulation in enclosed spaces and trigger alarms for leaks. In chlor-alkali plants, emissions from electrolytic cells and decomposers are minimized by reusing vent gases internally or neutralizing residuals in alkaline , with overall fugitive Cl₂ losses typically below 0.5% of production. Regulatory frameworks, such as the U.S. EPA's standards under 40 CFR 266.107, control chlorine emissions from combustors by limiting total chlorine and feed rates to maintain stack emissions below health-based screening limits, calculated as functions of stack height and terrain. For mercury-cell chlor-alkali plants, the EPA has proposed Cl₂ emission standards to address uncontrolled releases, alongside phasing out mercury emissions, reflecting a shift to membrane-cell that reduces both mercury and chlorine losses. Exposure control plans mandated by agencies like OSHA and require facility-specific procedures, including emergency shutoffs and , to limit worker and ambient exposures below permissible ceilings of 1 ppm. Byproduct formation arises prominently during chlorine's use in disinfection, where Cl₂ reacts with natural (NOM) such as humic acids to produce disinfection byproducts (DBPs) including trihalomethanes (THMs) like and haloacetic acids (HAAs). These reactions occur via and addition mechanisms, with DBP yields depending on , temperature, contact time, and NOM concentration; for instance, chlorination of surface waters with 2-5 mg/L TOC can generate 50-200 μg/L THMs. Certain DBPs, particularly brominated THMs, exhibit and have been associated in epidemiological studies with elevated risk, though causation remains unproven and confounded by factors like smoking. In industrial contexts, chlorine production byproducts include trace organochlorines from impurities in brine feedstocks, potentially forming persistent pollutants if not controlled, while wastewater chlorination generates toxic drug-derived DBPs in effluents. Mitigation strategies for DBPs involve enhanced coagulation or activated carbon adsorption to remove precursors prior to chlorination, alongside regulated limits under EPA's National Primary Drinking Water Regulations, capping TTHMs at 80 μg/L and HAA5 at 60 μg/L as running annual averages. Empirical assessments indicate that chlorination's pathogen inactivation benefits—preventing waterborne diseases responsible for historical mortality rates exceeding 10% in untreated systems—outweigh DBP risks at regulated levels, with no conclusive evidence of population-level harm from compliant exposures. Alternative disinfectants like chloramines reduce THM formation but may increase N-nitrosodimethylamine, highlighting trade-offs in byproduct profiles.

Regulatory Frameworks and Mitigation

The (OSHA) regulates workplace exposure to chlorine gas under 29 CFR 1910.1000, establishing a (PEL) of 0.5 parts per million (ppm) as an 8-hour time-weighted average and a (STEL) of 1 ppm for 15 minutes. The Environmental Protection Agency (EPA), in coordination with OSHA, addresses chlorine under the Toxic Substances Control Act (TSCA) for industrial uses, requiring assessments and controls for releases, though chlorine itself is not subject to the same phase-out mandates as certain chlorinated solvents like . For public water systems, the EPA's Stage 1 Disinfectants and Disinfection Byproducts Rule (DBPR), finalized December 16, 1998, sets a maximum residual level (MRDL) of 4.0 milligrams per liter (mg/L) for chlorine and maximum contaminant levels (MCLs) of 80 micrograms per liter (μg/L) for total trihalomethanes (TTHMs) and 60 μg/L for haloacetic acids (five) (HAA5), with Stage 2 DBPR enhancements in 2006 mandating improved monitoring at points of maximum occurrence to reduce variability in exposure. Transportation of chlorine falls under the U.S. (DOT) Hazardous Materials Regulations (49 CFR Parts 100-185), classifying it as UN 1017, a Division 2.3 gas with subsidiary risks of oxidizer (5.1) and corrosive (8), requiring placarding on vehicles, specialized like ton containers or tank cars equipped with safety valves and fusible plugs per 49 CFR 173.314, and attendance by a qualified person during unloading except for brief periods. Internationally, the Model Regulations (20th revised edition, 2023) align with DOT via the Globally Harmonized System (GHS), mandating hazard pictograms for and oxidation, while the International Maritime (IMDG) Code specifies segregation and ventilation for chlorine shipments. Mitigation strategies emphasize over reliance on . In industrial facilities, emission controls include wet scrubbers using to neutralize chlorine gas into solutions, achieving capture efficiencies above 99% under Clean Air Act permits, alongside continuous monitoring with electrochemical sensors calibrated to OSHA PELs. For , DBP formation is mitigated by precursor removal via enhanced with dosing (typically 20-50 mg/L) prior to chlorination, or switching to alternative disinfectants like (maintaining 1-4 mg/L total chlorine residual) or (UV) irradiation at doses of 20-40 mJ/cm², which reduces THM yields by up to 90% without forming chlorinated byproducts. Emergency response protocols, such as those from the Chlorine Institute, recommend immediate area evacuation, wind-directed downwind protection, and neutralization with 10% solutions for spills exceeding 10 pounds. These measures prioritize causal of chlorine's reactivity—rooted in its and oxidation potential of 1.36 V—while empirical data from incident analyses confirm their efficacy in averting large-scale releases, as seen in post-2005 rail car standards reducing leak probabilities.

Economic and Societal Dimensions

Global chlorine production is dominated by the chlor-alkali process, primarily using membrane cell technology in modern facilities, with total output projected to reach 80.62 million metric tons in 2025. Asia Pacific leads as the largest producing and consuming region, accounting for over half of global capacity due to rapid industrialization and demand for downstream products like polyvinyl chloride (PVC). China, the top producer, alongside the United States, Europe, and Japan, collectively represent about 85% of worldwide production. In Europe, production totaled approximately 10 million metric tons in 2023, with Germany holding the highest capacity at nearly 5.5 million metric tons as of 2022. Major producers include companies such as , , AG, and Hanwha Chemical, which operate large-scale facilities integrated with caustic soda and co-production. The maintains significant output through firms like , focusing on chlorine derivatives including PVC. Export dynamics highlight as a leading exporter with $140 million in shipments in 2023, followed by and , reflecting regional trade patterns influenced by proximity to North American and European markets. Market trends indicate steady growth at a (CAGR) of around 4-5% through 2030, driven by expanding applications in disinfection, pharmaceuticals, and plastics . The global market value is estimated at $44.05 billion in 2025, rising to $68.11 billion by 2033, with PVC demand in and as key factors. Challenges include high energy costs for and regulatory pressures on emissions, prompting shifts toward energy-efficient processes over older mercury cells. Supply chain vulnerabilities, such as those exposed by the 2022 in , have led to production curtailments, underscoring the commodity's sensitivity to raw material salt availability and prices.

Contributions to Public Health and Industry

Chlorine has played a pivotal role in through its use in disinfection, beginning with the first municipal application in , on January 28, 1908, which marked the start of widespread chlorination to combat waterborne pathogens. This innovation drastically reduced incidences of diseases such as typhoid, , and ; by the mid-20th century, chlorination contributed to averting an estimated 9 billion cases of waterborne illness in the United States alone. Empirical data from early 20th-century U.S. vital statistics indicate that improvements in sanitation, including chlorination, accounted for approximately 75% of the decline in and 66% in between 1900 and 1940. In developing regions, point-of-use chlorination has similarly demonstrated effectiveness, with meta-analyses showing a 29% reduction in risk among children under five years old. These outcomes stem from chlorine's residual disinfectant properties, which maintain microbial control in distribution systems unlike non-residual alternatives. Beyond , chlorine compounds enable in swimming pools and , preventing outbreaks of recreational water illnesses; for instance, proper chlorination maintains free chlorine residuals of 1-3 mg/L, effectively inactivating like and viruses. Household-level applications, such as solutions, further extend these benefits in low-resource settings, where randomized trials confirm sustained reductions in child morbidity from contaminated sources. In industry, chlorine serves as a foundational chemical feedstock, with global production exceeding 80 million metric tons annually as of recent estimates, primarily via the chlor-alkali process that co-produces . Key applications include the synthesis of (PVC), which consumed about 36% of U.S. chlorine output in 2006 for piping, construction, and packaging materials valued in billions. Other sectors leverage chlorine for producing inorganic compounds (e.g., for metal ) and organics like solvents and pharmaceuticals, underpinning markets projected to grow from USD 35.75 billion in 2023 to USD 53.88 billion by 2030 at a 5.9% CAGR. In the U.S., chlorine-derived products and processes support over $175 billion in economic output and 441,000 jobs, with direct contributions exceeding $46 billion yearly through enhanced manufacturing efficiency in textiles, paper, and disinfectants. These industrial roles amplify indirectly by enabling sterile medical devices and products, while the co-production of caustic soda facilitates aluminum refining and soap manufacturing.

References

  1. https://www.coastalwiki.org/wiki/Organochlorine_compounds
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