Arsenate-based pesticides such as lead hydrogen arsenate were commonly used until their replacement by newer pesticides such as DDT and subsequent ban by multiple regulatory bodies due to health concerns.[8][9]
Pourbaix diagram showing the distribution of arsenate and arsenite species in water. Oxygenated waters have a high pe value and arsenate species dominate. In deoxygenated water, with low pe, arsenite species dominate.[16][17]
Depending on the pH, arsenate can be found as trihydrogen arsenate (that is arsenic acidH3AsO4), dihydrogen arsenate (H2AsO−4), hydrogen arsenate (HAsO2−4), or arsenate (AsO3−4).[18] Trihydrogen arsenate is also known as arsenic acid. At a given pH, the distribution of these arsenate species can be determined from their respective acid dissociation constants.[17]
H3AsO4 + H2O ⇌ H2AsO−4 + [H3O]+(pKa1 = 2.19)
H2AsO−4 + H2O ⇌ HAsO2−4 + [H3O]+(pKa2 = 6.94)
HAsO2−4 + H2O ⇌ AsO3−4 + [H3O]+(pKa3 = 11.5)
These values are similar to those of phosphoric acid. Hydrogen arsenate and dihydrogen arsenate predominate in aqueous solution near neutral pH.[17]
The reduction potential (pe) of a solution also affects arsenate speciation. In natural waters, the dissolved oxygen content is the main factor influencing reduction potential. Arsenates occur in oxygenated waters, which have a high pe, while arsenites are the main arsenic species in anoxic waters with a low pe.[16]
A Pourbaix diagram shows the combined influence of pH and pe on arsenate speciation.
Arsenates, along with arsenites, are a significant source of contamination in some natural water sources and can lead to arsenic poisoning with repeated exposure.[19][20] Countries with high levels of arsenic minerals in sediment and rock, such as Bangladesh, are especially at risk of arsenate contamination.[21][20]
As with other arsenic compounds, arsenate binds to lipoic acid, inhibiting the conversion of pyruvate into acetyl-CoA, blocking the Krebs cycle and therefore resulting in further loss of ATP.[23]
^Waalkes, Michael P. (2019), Baan, Robert A.; Stewart, Bernard W.; Straif, Kurt (eds.), "Arsenic and metals", Tumour Site Concordance and Mechanisms of Carcinogenesis, IARC Scientific Publications, Lyon (FR): International Agency for Research on Cancer, ISBN978-92-832-2217-0, PMID33979075, retrieved 2 April 2023{{citation}}: CS1 maint: work parameter with ISBN (link)
^ abPollutants, National Research Council (US) Committee on Medical and Biological Effects of Environmental (1977). Chemistry of Arsenic. National Academies Press (US).
^ abcBarton, C. (1 January 2014), "CCA-Treated Wood", in Wexler, Philip (ed.), Encyclopedia of Toxicology (Third Edition), Oxford: Academic Press, pp. 751–752, ISBN978-0-12-386455-0, retrieved 10 April 2023
^Pollutants, National Research Council (US) Committee on Medical and Biological Effects of Environmental (1977). Chemistry of Arsenic. National Academies Press (US).
^Sánchez-Rodas, Daniel; Luis Gómez-Ariza, José; Giráldez, Inmaculada; Velasco, Alfredo; Morales, Emilio (1 June 2005). "Arsenic speciation in river and estuarine waters from southwest Spain". The Science of the Total Environment. 345 (1–3): 207–217. Bibcode:2005ScTEn.345..207S. doi:10.1016/j.scitotenv.2004.10.029. ISSN0048-9697. PMID15919540.
^ ab"Arsenic". www.who.int. Retrieved 15 April 2023.