Potential environmental fate of elsinochrome A, a perylenequinone toxin produced in culture by bindweed biocontrol fungus Stagonospora convolvuli LA39

被引:9
作者
Ahonsi M.O. [1 ,2 ]
Boss D. [1 ]
Maurhofer M. [1 ]
Défago G. [1 ]
机构
[1] Phytopathology Group, Institute of Plant Sciences, Swiss Federal Institute of Technology, CH-8092, Zürich
[2] River Basin Research Center, Gifu University, Gifu 501-1193
来源
Environmentalist | 2006年 / 26卷 / 3期
关键词
Biological control agents (BCAs); Convolvulus; Environmental contamination and toxicity; Fungal metabolites; High performance liquid chromatography (HPLC); Photo-degradation; Photo-sensitizers; Photolysis; Risk assessment; Stability;
D O I
10.1007/s10669-006-7830-0
中图分类号
学科分类号
摘要
The photosensitizing perylenequinone toxin elsinochrome A (EA) is produced in culture by the bindweed biocontrol fungus Stagonospora convolvuli LA39 where it apparently plays a pathogenicity related role. We investigated the fate of EA with reference to its stability under different temperature and light conditions. EA remained stable when boiled in water at 100°C for 2 h. Similarly, exposing EA to 3-27°C in the dark for up to 16 weeks did not affect its stability either in dry or in aqueous form. However, results from irradiation experiments indicate that direct photolysis may be a significant degradation pathway for EA in the environment. EA either in dry form or dissolved in water was degraded by different irradiation wavelengths and intensities, with degradation plots fitting a first order rate kinetics. EA degraded faster if exposed in aqueous form, and at higher quantum flux density (μmol s-1 m-2). Sunlight was more effective in degrading EA than artificial white light and ultraviolet radiations (UV-A or UV-B). Exposing EA to natural sunlight, particularly, during the intense sunshine (1,420- 1,640 μmol s-1 m-2) days of 30 July to 5 August 2004 in Zurich caused the substance to degrade rapidly with half-life under such condition only 14 h. This implies that should EA gets into the environment, particularly on exposed environmental niches, such as on plant surfaces through biocontrol product spray, or released from shed diseased leaves, it may have no chance of accumulating to 'level of concern'. Furthermore, a toxicity assay using Trichoderma atroviride P1 as biosensor showed that photo-degraded EA was not toxic, indicating that no stable toxic by-products were left. © Springer Science + Business Media, LLC 2006.
引用
收藏
页码:183 / 193
页数:10
相关论文
共 40 条
[11]  
Carson R., Silent Spring, (1962)
[12]  
Chen C.T., Nakanishi K., Natori S., Biosynthesis of Elsinochrome A, the Perylenequinone from Elsinoe spp. 1, Chemical and Pharmaceutical Bulletin, 14, pp. 1434-1437, (1966)
[13]  
Chu F.S., Li G.Y., Simultaneous Occurrence of Fumonisin B1 and other mycotoxins in moldy corn collected from people's Republic of China in Regions of High Incidences of Esophageal Cancer, Applied and Environmental Microbiology, 60, pp. 847-852, (1994)
[14]  
Chu F.S., Chang C.C., Ashoor S.H., Prentice N., Stability of aflatoxin B1 and ochratoxin Ain Brewing, Applied Microbiology, 29, pp. 313-316, (1975)
[15]  
Daub M.E., Ehrenshaft M., The photoactivated toxin cercosporin as a tool in fungal photobiology, Physiologia Plantarum, 89, pp. 227-236, (1993)
[16]  
Daub M.E., Ehrenshaft M., The photoactive cercospora toxin cercosporin: Contributions to plant disease and fundamental Biology, Annual Review of Phytopathology, 38, pp. 461-490, (2000)
[17]  
Daub M.E., Cercosporin, a photosensitizing toxin from Cercospora species, Phytopathology, 72, pp. 370-374, (1982)
[18]  
Jensen-Korte U., Anderson C., Spiteller M., Photodegradation of pesticides in the presence of humic substances, The Science of the Total Environment, 62, pp. 335-340, (1987)
[19]  
Joffe A.Z., Fusarium Species: Their Biology and Toxicology, (1986)
[20]  
Katagi T., Photodegradation of pesticides on plant and soil surfaces, Reviews of Environmental Contamination and Toxicology, 182, pp. 1-195, (2004)