Spallholz J E
College of Human Sciences, Texas Tech University, Lubbock.
Free Radic Biol Med. 1994 Jul;17(1):45-64. doi: 10.1016/0891-5849(94)90007-8.
Selenium toxicity was first confirmed in 1933 to occur in livestock that consumed plants of the genus Astragalus, Xylorrhiza, Oonopsis, and Stanleya in the western regions of the United States. In 1957 selenium was identified as an essential nutrient for laboratory rats and soon thereafter for chickens and sheep. Essentiality for mammalian species was established in 1973 with the discovery that the enzyme glutathione peroxidase contained selenium. During this same period of time, human epidemiological evidence suggested that selenium possessed anticarcinogenic effects. Since the 1970s, many animal studies have confirmed the human epidemiologic evidence that selenium compounds possess carcinostatic activity. Less progress has been made in explaining why many of these compounds of selenium are toxic and why these same compounds are carcinostatic. In 1988 the observation was made that oxidation of glutathione by selenite produced superoxide, opening a new area for selenium research. This present paper, drawing information from the literature on selenium metabolism in plants and animals, selenium toxicology, selenium cytotoxicity, and selenium carcinostatic activity in animals over the last sixty years, sets forth a probable biochemical catalytic mechanism that encompasses both selenium toxicity and selenium carcinostatic activity. The thesis presented here for scrutiny is that compounds of selenium are toxic owing to their prooxidant catalytic activity to produce superoxide (O2.-), hydrogen peroxide, and very likely other cascading oxyradicals. The toxicity of selenium compounds is countered by plant and animal methylation reactions and antioxidant defenses. As carcinostasis is mostly known to occur at supranutritional levels of selenium in animals, carcinostasis appears to be directly correlated to selenium toxicity. The catalytic toxic selenium specie appears to be the metabolic selenide (RSe-) anion.
1933年,人们首次证实美国西部地区的牲畜因食用黄芪属、裂根草属、卵叶草属和斯坦利草属植物而出现硒中毒现象。1957年,硒被确定为实验大鼠的必需营养素,此后不久又被确定为鸡和羊的必需营养素。1973年,随着谷胱甘肽过氧化物酶含有硒这一发现,确定了硒对哺乳动物的必要性。在同一时期,人类流行病学证据表明硒具有抗癌作用。自20世纪70年代以来,许多动物研究证实了人类流行病学证据,即硒化合物具有抗癌活性。在解释为什么许多这些硒化合物有毒以及为什么这些相同的化合物具有抗癌作用方面,进展较小。1988年,有人观察到亚硒酸盐氧化谷胱甘肽会产生超氧化物,这为硒研究开辟了一个新领域。本文借鉴了过去60年中有关植物和动物体内硒代谢、硒毒理学、硒细胞毒性以及动物体内硒抗癌活性的文献资料,提出了一种可能的生化催化机制,该机制涵盖了硒毒性和硒抗癌活性。这里提出供审查的论点是,硒化合物有毒是由于它们具有产生超氧化物(O2.-)、过氧化氢以及很可能还有其他级联氧自由基的促氧化催化活性。植物和动物的甲基化反应及抗氧化防御可对抗硒化合物的毒性。由于大多数已知抗癌作用发生在动物体内硒的超营养水平,因此抗癌作用似乎与硒毒性直接相关。具有催化毒性的硒物种似乎是代谢性硒化物(RSe-)阴离子。