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Critical temperature || 1673
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Arsenic (
IPA: , ) is a
chemical element that has the symbol
As and
atomic number 33. Arsenic was discovered by Albertus Magnus (Germany) in 1250. Its Atomic Mass is 74.92. Its Ionic Charge is (3-) Its position in the periodic table is shown at right. This is a notoriously poisonous
metalloid that has many
allotropic forms: yellow (molecular non-metallic) and several black and gray forms (metalloids) are a few that are seen. Three metalloidal forms of arsenic with different crystal structures are found free in nature (the minerals arsenic ''sensu strictu'' and the much rarer arsenolamprite and pararsenolamprite), but it is more commonly found as arsenide and arsenate compounds. Several hundred such mineral species are known. Arsenic and its compounds are used as
pesticides,
herbicides,
insecticides and various
alloys.
The most common
oxidation states for arsenic are -3 (arsenides: usually alloy-like intermetallic compounds), +3 (arsenates(III) or arsenites, and most organoarsenic compounds), and +5 (arsenates(V): the most stable inorganic arsenic oxycompounds). Arsenic also bonds readily to itself, forming, for instance, As-As pairs in the red sulfide
realgar and square As
43- ions in the arsenide skutterudite. In the +3 oxidation state, the stereochemistry of arsenic is affected by possession of a
lone pair of
electrons.
Notable characteristics
Arsenic is very similar chemically to its predecessor,
phosphorus. Similar to phosphorus, it forms colourless, odourless, crystalline oxides As
2O
3 and As
2O
5 which are hygroscopic and readily soluble in water to form acidic solutions. Arsenic (V) acid, like phosphoric acid, is a weak acid. Like phosphorus, arsenic forms an unstable, gaseous hydride: arsine (AsH
3). The similarity is so great that arsenic will partly substitute for phosphorus in biochemical reactions and is thus
poisonous. However, in subtoxic doses, soluble arsenic compounds act as
stimulants, and were once popular in small doses as medicinals by people in the mid 18th century.
When heated in air it
oxidizes to
arsenic trioxide; the fumes from this reaction have an odor resembling
garlic. This odor can be detected on striking arsenide minerals such as
arsenopyrite with a hammer. Arsenic and some arsenic compounds can also
sublime upon heating, converting directly to a gaseous form without an intervening liquid state. Elemental arsenic is found in many solid forms: the yellow form is soft, waxy and unstable, and is made of tetrahedral As
4 molecules similar to the molecules of white phosphorus. The gray, black or 'metallic' forms have somewhat layered crystal structures with bonds extending throughout the crystal. They are brittle
semiconductors with a metallic luster. The
density of the yellow form is 1.97 g/cm³; rhombohedral 'gray arsenic' is much denser with a density of 5.73 g/cm³; the other metalloidal forms are similarly dense.
Applications
Lead hydrogen arsenate has been used, well into the 20th century, as an
insecticide on
fruit trees (sometimes resulting in
brain damage to those working the sprayers), and
Scheele's Green (a copper arsenate) has even been recorded in the 19th century as a
coloring agent in
sweets. In the last half century,
monosodium methyl arsenate (MSMA), a less toxic organic form of arsenic, has replaced lead arsenate's role in agriculture.
The application of most concern to the general public is probably that of
wood which has been treated with
chromated copper arsenate ("CCA", or "
Tanalith", and the vast majority of older "
pressure treated" wood). CCA timber is still in widespread use in many countries, and was heavily used during the latter half of the 20th century as a structural, and outdoor
building material, where there was a risk of
rot, or
insect infestation in untreated timber. Although widespread bans followed the publication of studies which showed low-level leaching from in-situ timbers (such as children's
playground equipment) into surrounding
soil, the most seriousrisk is presented by the burning of CCA timber. Recent years have seen fatal animal poisonings, and serious human poisonings resulting from the ingestion - directly or indirectly - of wood ash from CCA timber (the lethal human dose is approximately 20 grams of ash). Scrap CCA construction timber continues to be widely burnt through ignorance, in both commercial and domestic fires. Protocols for safe disposal of CCA timber are still in place only patchily; there is concern in some quarters about the widespread
landfill disposal of such timber.
During the 18th, 19th, and 20th centuries, a number of arsenic compounds have been used as medicines, including
arsphenamine (by
Paul Ehrlich) and
arsenic trioxide (by Thomas Fowler).
Arsphenamine as well as
Neosalvarsan was indicated for
syphilis and
trypanosomiasis, but has been superseded by modern
antibiotics.
Arsenic trioxide has been used in a variety of ways over the past 200 years, but most commonly in the treatment of
cancer. The
Food and Drug Administration in 2000 approved this compound for the treatment of patients with
acute promyelocytic leukemia that is resistant to
ATRA.
[Antman, Karen H. (2001). The History of Arsenic Trioxide in Cancer Therapy . Introduction to a supplement to ''The Oncologist''. 6 (Suppl 2), 1-2. PMID 11331433.] It was also used as
Fowler's solution in
psoriasis.
[Huet ''et.al''. Noncirrhotic presinusoidal portal hypertension associated with chronic arsenical intoxication. ''Gastroenterology'' 1975;68(5 Pt 1):1270-7.]
PMID 1126603
Copper acetoarsenite was used as a green
pigment known under many different names, including '
Paris Green' and 'Emerald Green'. It caused numerous
arsenic poisonings.
Other uses;
Various agricultural insecticides, termination and poisons.
Used in animal feed, particularly in the US as a method of disease prevention and growth stimulation.
Gallium arsenide is an important semiconductor material, used in integrated circuits. Circuits made using the compound are much faster (but also much more expensive) than those made in silicon. Unlike silicon it is direct bandgap, and so can be used in laser diodes and LEDs to directly convert electricity into light.
Also used in bronzing and pyrotechny.
Occupational Exposures
Exposure to higher-than-average levels of arsenic can occur in some occupations placing workers at risk. Industries that use inorganic arsenic and its compounds include wood preservation, glass production, nonferrous metal alloys, and electronic semiconductor manufacturing. Inorganic arsenic is also found in coke oven emissions associated with the smelter industry.
History
The word ''arsenic'' is borrowed from the
Persian word زرنيخ ''Zarnikh'' meaning "yellow
orpiment". ''Zarnikh'' was borrowed by
Greek as ''arsenikon''. Arsenic has been known and used in
Persia and elsewhere since ancient times. As the symptoms of
arsenic poisoning were somewhat ill-defined, it was frequently used for
murder until the advent of the
Marsh test, a sensitive chemical test for its presence. (Another less sensitive but more general test is the
Reinsch test.) Due to its use by the ruling class to murder one another and its potency and discreetness, arsenic has been called the ''Poison of Kings and the King of Poisons''.
During the
Bronze Age, arsenic was often included in
bronze, which made the alloy harder (so-called "
arsenical bronze").
Albertus Magnus (Albert the Great, 1193-1280) is believed to have been the first to isolate the
element in 1250. In 1649
Johann Schröder published two ways of preparing arsenic.
In the
Victorian era, 'arsenic' (colourless, crystalline, soluble 'white arsenic') was mixed with
vinegar and
chalk and eaten by women to improve the
complexion of their faces, making their skin paler to show they did not work in the fields. Arsenic was also rubbed into the faces and arms of women to 'improve their complexion'. The accidental use of arsenic in the adulteration of foodstuffs led to
the Bradford sweet poisoning in 1858, which resulted in approximately 20 deaths and 200 people taken ill with arsenic poisoning.
Arsenic in drinking water
Arsenic contamination of groundwater has led to a massive epidemic of arsenic poisoning in
Bangladesh[Andrew Meharg, Venomous Earth - How Arsenic Caused The World's Worst Mass Poisoning, Macmillan Science , 2005.] and neighbouring countries. It is estimated that approximately 57 million people are drinking
groundwater with arsenic concentrations elevated above the
World Health Organization's standard of 10
parts per billion. The arsenic in the groundwater is of natural origin, and is released from the sediment into the groundwater due to the anoxic conditions of the subsurface. This groundwater began to be used after western
NGOs instigated a massive tube
well drinking-water program in the late
twentieth century. This program was designed to prevent drinking of bacterially contaminated surface waters, but failed to test for arsenic in the groundwater.(2) Many other countries and districts in
South East Asia, such as
Vietnam,
Cambodia, and
Tibet,
China, are thought to have geological environments similarly conducive to generation of high-arsenic groundwaters.
Arsenicosis was reported in
Nakhon Si Thammarat,
Thailand in 1987, and the dissolved arsenic in the
Chao Phraya River is suspected of containing high levels of naturally occurring arsenic, but has not been a public health problem due to the use of bottled water.
[http://wedc.lboro.ac.uk/conferences/pdfs/28/Kohnhorst.pdf]
The northern United States, including parts of
Michigan,
Wisconsin,
Minnesota and the Dakotas are known to have significant concentrations of arsenic in ground water.
Arsenic can be removed from drinking water through
coprecipitation of iron minerals by oxidation and filtering. When this treatment fails to produce acceptable results, adsorptive arsenic removal media may be utilized. Several adsorptive media systems have been approved for point of service use in a study funded by the
United States Environmental Protection Agency (U.S.EPA) and the
National Science Foundation (NSF).
Magnetic separations of arsenic at very low magnetic field gradients have been demonstrated in point-of-use water purification with high–surface area and monodisperse
magnetite (Fe
3O
4)
nanocrystals. Using the high specific surface area of Fe
3O
4 nanocrystals the mass of waste associated with arsenic removal from water has been dramatically reduced.
[Yavuz et al., Low-Field Magnetic Separation of Monodisperse Fe3O4 Nanocrystals Science , 2005.]
Occurrence
In 2005, China was the top producer of white arsenic with almost 50% world share followed by Chile and Peru, reports the
British Geological Survey.
Arsenopyrite also unofficially called mispickel (
FeAs
S) is the most common arsenic-bearing
mineral. On roasting in air, the arsenic sublimes as arsenic (III) oxide leaving iron oxides.
The most important compounds of arsenic are arsenic (III) oxide, As
2O
3, ('
white arsenic'), the yellow sulfide
orpiment (As
2S
3) and red
realgar (As
4S
4),
Paris Green,
calcium arsenate, and
lead hydrogen arsenate. The latter three have been used as
agricultural insecticides and
poisons. Orpiment and realgar were formerly used as painting pigments, though they have fallen out of use due to their toxicity and reactivity. Although arsenic is sometimes found native in nature, its main economic source is the mineral
arsenopyrite mentioned above; it is also found in arsenides of metals such as
silver,
cobalt (cobaltite: CoAsS and skutterudite: CoAs
3) and
nickel, as
sulfides, and when oxidised as arsenate minerals such as
mimetite, Pb
5(AsO
4)
3Cl and
erythrite, Co
3(AsO
4)
2. 8H
2O, and more rarely arsenites ('arsenite' = arsenate(III), AsO
33- as opposed to arsenate (V), AsO
43-).
In addition to the inorganic forms mentioned above, arsenic also occurs in various organic forms in the environment. Inorganic arsenic and its compounds, upon entering the
food chain, are progressively metabolised to a less toxic form of arsenic through a process of
methylation.
Nickernuts are said to contain arsenic.
''See also
Arsenide minerals,
Arsenate minerals.''
Toxicity
Arsenic and many of its compounds are especially potent poisons. Arsenic disrupts
ATP production through several mechanisms. At the level of the citric acid cycle, arsenic inhibits
pyruvate dehydrogenase and by competing with phosphate it uncouples
oxidative phosphorylation, thus inhibiting energy-linked reduction of
NAD+, mitochondrial respiration, and ATP synthesis. Hydrogen peroxide production is also increased, which might form reactive oxygen species and oxidative stress. These metabolic interferences lead to death from multi-system
organ failure (see
arsenic poisoning) probably from
necrotic cell death, not
apoptosis. A
post mortem reveals brick red colored
mucosa, due to severe
hemorrhage. Although arsenic causes toxicity, it can also play a protective role.
[Casarett and Doull's Essentials of Toxicology 2003].
Elemental arsenic and arsenic compounds are classified as "
toxic" and "dangerous for the environment" in the
European Union under
directive 67/548/EEC.
The
IARC recognizes arsenic and arsenic compounds as
group 1 carcinogens, and the EU lists
arsenic trioxide,
arsenic pentoxide and
arsenate salts as category 1
carcinogens.
Arsenic is known to cause
arsenicosis due to its manifestation in drinking water, “the most common species being arsenate
; As(V) and arsenite
; As(III) ”. The ability of arsenic to undergo redox conversion between As(III) and As(V) makes its availability in the environment possible. According to Croal, Gralnick, Malasarn, and Newman, “
the understanding
of what stimulates As(III) oxidation and/or limits As(V) reduction is relevant for bioremediation of contaminated sites (Croal). The study of chemolithoautotrophic As(III) oxidizers and the heterotrophic As(V) reducers can help the understanding of the oxidation and/or reduction of arsenic.
[Croal, Laura R., Jeffrey A. Gralnick, Davin Malasarn, and Dianne K. Newman. "The Genetics of Geochemisty." Annual Review of Genetics 38.1 (2004): 175-206. 24 April, 2006. ]
Isotopes
Arsenic has been proposed as a "
salting" material for
nuclear weapons (
cobalt is another, better-known salting material). A jacket of
75As, irradiated by the intense high-energy neutron flux from an exploding thermonuclear weapon, would transmute into the radioactive isotope
76As with a
half-life of 1.0778 days and produce approximately 1.13
MeV of
gamma radiation, significantly increasing the radioactivity of the weapon's
fallout for several hours.Such a weapon is not known to have ever been built, tested, or used.