Arsenic biochemistry
Arsenic biochemistry refers to
Sources of arsenic
Organoarsenic compounds in nature
The evidence that arsenic may be a beneficial nutrient at trace levels below the background to which living organisms are normally exposed has been reviewed.
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Arsenobetaine, one of the most common arsenic compound in nature. Also common is arsenocholine, which has CH2OH in place of CO2H).
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Trimethylarsine, produced by microbial action on arsenate-derived pigments
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Arsenic-containing ribose derivatives (R = several groups)
A topical source of arsenic are the green pigments once popular in wallpapers, e.g. Paris green. A variety of illness have been blamed on this compound, although its toxicity has been exaggerated.[10]
Trimethylarsine, once known as Gosio's gas, is an intensely malodorous organoarsenic compound that is commonly produced by microbial action on inorganic arsenic substrates.[11]
Arsenic (V) compounds are easily reduced to arsenic (III) and could have served as an electron acceptor on primordial Earth.
Incorrect claims of arsenic-based life (phosphorus substitution)
Although phosphate and arsenate are structurally similar, there is no evidence that arsenic replaces phosphorus in DNA or RNA.[13] A 2010 experiment involving the bacteria GFAJ-1 that made this claim was refuted by 2012.[14][15]
Anthropogenic arsenic compounds
Anthropogenic (man-made) sources of arsenic, like the natural sources, are mainly arsenic oxides and the associated anions. Man-made sources of arsenic, include wastes from mineral processing, swine and poultry farms.[16] For example, many ores, especially sulfide minerals, are contaminated with arsenic, which is released in roasting (burning in air). In such processing, arsenide is converted to arsenic trioxide, which is volatile at high temperatures and is released into the atmosphere. Poultry and swine farms make heavy use of the organoarsenic compound roxarsone as an antibiotic in feed.[17][18] Some wood is treated with copper arsenates as a preservative. The mechanisms by which these sources affect "downstream" living organisms remains uncertain but are probably diverse. One commonly cited pathway involves methylation.[19]
The monomethylated acid, methanearsonic acid (CH3AsO(OH)2), is a precursor to fungicides (tradename Neoasozin) in the cultivation of rice and cotton. Derivatives of
Arsenic-based drugs
Despite, or possibly because of, its long-known toxicity, arsenic-containing potions and drugs have a history in
Methylation of arsenic
Inorganic arsenic and its compounds, upon entering the food chain, are progressively metabolised (detoxified) through a process of methylation.[19] The methylation occurs through alternating reductive and oxidative methylation reactions, that is, reduction of pentavalent to trivalent arsenic followed by addition of a methyl group (CH3).[24]
In mammals, methylation occurs in the liver by
There are two major forms of arsenic that can enter the body, arsenic (III) and arsenic (V).[26] Arsenic (III) enters the cells though aquaporins 7 and 9, which is a type of aquaglyceroporin.[26] Arsenic (V) compounds use phosphate transporters to enter cells.[26] The arsenic (V) can be converted to arsenic (III) by the enzyme purine nucleoside phosphorylase.[26] This is classified as a bioactivation step, as although arsenic (III) is more toxic, it is more readily methylated.[27]
There are two routes by which inorganic arsenic compounds are methylated.[28] The first route uses Cyt19 arsenic methyltransferase to methylate arsenic (III) to a mono-methylated arsenic (V) compound.[26] This compound is then converted to a mono-methylated arsenic (III) compound using Glutathione S-Transferase Omega-1 (GSTO1).[26] The mono-methylated arsenic (V) compound can then be methylated again by Cyt19 arsenic methyltransferase, which forms a dimethyl arsenic (V) compound, which can be converted to a dimethyl arsenic (III) compound by Glutathione S-Transferase Omega-1 (GTSO1).[26] The other route uses glutathione (GSH) to conjugate with arsenic (III) to form an arsenic (GS) 3 complex.[26] This complex can form a monomethylated arsenic (III) GS complex, using Cyt19 arsenic methyltransferase, and this monomethylated GS complex is in equilibrium with the monomethylated arsenic (III).[26] Cyt19 arsenic methyltransferase can methylate the complex one more time, and this forms a dimethylated arsenic GS complex, which is in equilibrium with a dimethyl arsenic (III) complex.[26] Both of the mono-methylated and di-methylated arsenic compounds can readily be excreted in urine.[27] However, the monomethylated compound was shown to be more reactive and more toxic than the inorganic arsenic compounds to human hepatocytes (liver), keratinocytes in the skin, and bronchial epithelial cells (lungs).[29]
Studies in experimental animals and humans show that both inorganic arsenic and methylated metabolites cross the placenta to the fetus, however, there is evidence that methylation is increased during pregnancy and that it could be highly protective for the developing organism.[30]
Enzymatic methylation of arsenic is a detoxification process; it can be methylated to methylarsenite, dimethylarsenite or trimethylarsenite, all of which are trivalent. The methylation is catalyzed by arsenic methyltransferase (AS3MT) in mammals, which transfers a methyl group on the cofactor S-adenomethionine (SAM) to arsenic (III). An orthologue of AS3MT is found in bacteria and is called CmArsM. This enzyme was tested in three states (ligand free, arsenic (III) bound and SAM bound). Arsenic (III) binding sites usually use thiol groups of cysteine residues. The catalysis involves thiolates of Cys72, Cys174, and Cys224. In an SN2 reaction, the positive charge on the SAM sulfur atom pulls the bonding electron from the carbon of the methyl group, which interacts with the arsenic lone pair to form an As−C bond, leaving SAH.[31]
Excretion
In humans, the major route of excretion of most arsenic compounds is via the urine. The biological half-life of inorganic arsenic is about 4 days, but is slightly shorter following exposure to arsenate than to arsenite. The main metabolites excreted in the urine of humans exposed to inorganic arsenic are mono- and dimethylated arsenic acids, together with some unmetabolized inorganic arsenic.[25]
The biotransformation of arsenic for excretion is primarily done through the nuclear factor erythroid 2 related factor 2 (
This adduct can also decompose back into inorganic arsenic.Of particular note in the excretion of arsenic is the multiple methylation steps that take place which may increase the toxicity of arsenic[36] due to MMeAsIII being a potent inhibitor of glutathione peroxidase,[37] glutathione reductase, pyruvate dehydrogenase,[38] and thioredoxin reductase.[39]
Arsenic toxicity
Arsenic is a cause of mortality throughout the world; associated problems include heart, respiratory, gastrointestinal, liver, nervous and kidney diseases.[2][25]
Arsenic interferes with cellular longevity by
By contrast, arsenic oxide is an approved and effective chemotherapeutic drug for the treatment of acute promyelocytic leukemia (APL).[3]
Toxicity of pentavalent arsenicals
Due to its similar structure and properties, pentavalent arsenic metabolites are capable of replacing the phosphate group of many metabolic pathways.
Toxicity of trivalent arsenicals
Enzymes and receptors that contain thiol or
Oxidative stress
Arsenic can cause oxidative stress through the formation of
The reactive nitrogen species arise once the reactive oxygen species destroy the
DNA damage
Arsenic is reported to cause
Inhibition of DNA repair
Inhibition of DNA repair processes is considered one of main mechanism of inorganic arsenic genotoxicity. Nucleotide excision repair (NER) and base excision repair (BER) are the processes implicated in the repair of DNA base damage induced by ROS after arsenic exposure. In particular, the NER mechanism is the major pathway for repairing bulky distortions in DNA double helix, while the BER mechanism is mainly implicated in the repair of single strand breaks induced by ROS,[54][55][56][57] but inorganic arsenic could also repress the BER mechanism.[58][59][60]
Neurodegenerative mechanisms
Arsenic is highly detrimental to the innate and the adaptive immune system of the body.[61] When the amount of unfolded and misfolded proteins in endoplasmic reticulum stress is excessive, the unfolded protein response (UPR) is activated to increase the activity of several receptors that are responsible the restoration of homeostasis.[61] The inositol-requiring enzyme-1 (IRE1) and protein kinase RNA-like endoplasmic reticulum kinase (PERK) are two receptors that restrict the rate of translation.[61] On the other hand, the unfolded proteins are corrected by the production of chaperones, which are induced by the activating transcription factor 6 (ATF6).[61] If the number of erroneous proteins elevates, further mechanism is active which triggers apoptosis.[61] Arsenic has evidentially shown to increase the activity of these protein sensors.[61]
Immune dysfunction
Arsenic exposure in small children distorts the ratio of
Arsenic poisoning treatment
There are three molecules that serve as
When these agents
Other chelating agents can be used, but may cause more side effects than British Anti-Lewisite (BAL, Dimercaprol), succimer (
These drugs are efficient for acute poisoning of arsenic, which refers to the instantaneous effects caused by arsenic poisoning. For example, headaches, vomiting or sweating are some of the common examples of an instantaneous effect. In comparison, chronic poisonous effects arise later on, and unexpectedly such as organ damage. Usually it is too late to prevent them once they appear. Therefore, action should be taken as soon as acute poisonous effects arise.[64]
See also
- Arsenic compounds
- Extremophile
- Geomicrobiology
- Hypothetical types of biochemistry
- Organoarsenic chemistry
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