Lampi Mark A, Gurska Jolanta, McDonald Kristina I C, Xie Fangli, Huang Xiao-Dong, Dixon D George, Greenberg Bruce M
Department of Biology, University of Waterloo, Waterloo, Ontario N2L 3G1, Canada.
Environ Toxicol Chem. 2006 Apr;25(4):1079-87. doi: 10.1897/05-276r.1.
Polycyclic aromatic hydrocarbons (PAHs) are ubiquitous environmental contaminants known for their photoinduced toxicity. This toxicity may occur through two mechanisms: Photosensitization, and photomodification. Photosensitization generally leads to the production of singlet oxygen, a reactive oxygen species that is highly damaging to biological molecules. Photomodification of PAHs, usually via oxidation, results in the formation of new compounds and can occur under environmentally relevant levels of actinic radiation. The toxicities of 16 intact PAHs to Daphnia magna were assessed under two ultraviolet radiation conditions. The toxicity of intact PAHs generally increased in the presence of full-spectrum simulated solar radiation relative to that in the presence of visible light plus ultraviolet A only. Despite the knowledge of a bipartite mechanism of phototoxicity that includes photosensitization and photomodification, few studies have examined the effects of PAH photoproducts on animals. To expand the existing data, 14 PAH photoproducts (oxy-PAHs) also were assayed, most of which were highly toxic without further photomodification. Two photoproducts of benzo[a]pyrene, 1,6- and 3,6-benzo[a]pyrenequinone, were the most toxic compounds tested, followed closely by benz[a]anthraquinone. Each of these three compounds had a median effective concentration in the low nanomolar range. The data presented highlight the effects of ultraviolet radiation on mediating PAH toxicity and the need to analyze absorption spectra of contaminants in the prediction of photoinduced toxicity. The importance of the role of photomodification also is stressed, because several oxy-PAHs, an unregulated group of contaminants, were highly toxic to D. magna, a key bioindicator species in aquatic ecosystems.
多环芳烃(PAHs)是普遍存在的环境污染物,以其光诱导毒性而闻名。这种毒性可能通过两种机制发生:光致敏作用和光修饰作用。光致敏作用通常会导致单线态氧的产生,单线态氧是一种对生物分子具有高度破坏性的活性氧物种。PAHs的光修饰作用通常通过氧化发生,会导致新化合物的形成,并且可以在与环境相关的光化辐射水平下发生。在两种紫外线辐射条件下评估了16种完整PAHs对大型溞的毒性。相对于仅在可见光加紫外线A存在的情况下,完整PAHs的毒性在全光谱模拟太阳辐射存在时通常会增加。尽管已知光毒性的双重机制包括光致敏作用和光修饰作用,但很少有研究考察PAH光产物对动物的影响。为了扩充现有数据,还对14种PAH光产物(含氧PAHs)进行了测定,其中大多数在没有进一步光修饰的情况下具有高毒性。苯并[a]芘的两种光产物,1,6 - 和3,6 - 苯并[a]芘醌,是测试的毒性最大的化合物,紧随其后的是苯并[a]蒽醌。这三种化合物中的每一种的半数有效浓度都在低纳摩尔范围内。所呈现的数据突出了紫外线辐射对介导PAH毒性的影响以及在预测光诱导毒性时分析污染物吸收光谱的必要性。光修饰作用的重要性也得到了强调,因为几种含氧PAHs(一类未受监管的污染物)对大型溞(水生生态系统中的一种关键生物指示物种)具有高毒性。