Häkkinen Jani, Vehniäinen Eeva, Oikari Aimo
Department of Biological and Environmental Sciences, University of Jyväskylä, P.O. Box 35, FIN-40014, Jyväskylä, Finland.
Aquat Toxicol. 2003 Apr 10;63(2):159-71. doi: 10.1016/s0166-445x(02)00173-x.
Positively phototactic fish larvae may be exposed to increased ultraviolet-B (UV-B) radiation alone or, potentially and in addition, to polycyclic aromatic hydrocarbons (PAHs) such as retene (7-isopropyl-1-methylphenanthrene) at the egg or larval stages. Suspended and sedimental particulate material near pulp and paper mills may act as sources of retene in chemically contaminated lake areas. In laboratory conditions whitefish larvae were pre-exposed to retene (10, 32 and 100 microg/l), with relevant controls, and irradiated in semi-static tests for 3 h once a day (2 consecutive days) with two UV-B doses (CIE-weighted 2.8 or 5.4 kJ per m(2) per day) or with visible light only. These UV-B doses correspond with slightly subambient and 80% increases relative to the natural maximum daily doses of the solar UV-B in Finland in early May. The UV-B radiation alone increased mortality only slightly (2.7 and 4.0%, respectively). Similarly, no mortality was observed due to retene alone. On the contrary, simultaneous UV-B and retene exposure caused very high mortality to whitefish and all larvae died in the highest retene concentration. The photoinduced acute LC(50) for retene was 13.3 microg/l. Retene treated fish exhibited signs of behavioral irritation and hypoxia during and after the exposure to UV light. Severe skin damages were detected in larvae exposed simultaneously to retene and UV-B. The structural signs of sunburn could also be seen in UV-B and solvent controls (DMSO) with UV-B. Even at the lowest retene concentration, the number of mucous cells increased significantly in simultaneous chemical and UV-B treatment. We consider the tissue reaction as protective response against UV induced retene toxicity. Further, regarding liver parenchyma, fish exposed to retene with UV-B had lesions, revealing hepatotoxicity. We suggest that synergism of the UV-B radiation and the photoactivating pollutants such as retene is a potential risk factor to be taken into consideration in lake areas chemically contaminated by the pulp and paper industry.
具有正趋光性的鱼类幼体在鱼卵或幼体阶段可能单独受到增强的紫外线B(UV-B)辐射影响,或者此外还可能接触到多环芳烃(PAHs),如惹烯(7-异丙基-1-甲基菲)。纸浆和造纸厂附近的悬浮及沉积颗粒物质可能是化学污染湖泊区域中惹烯的来源。在实验室条件下,将白鲑幼体预先暴露于惹烯(10、32和100微克/升),设置相关对照,然后在半静态试验中每天照射一次,持续2天,每次照射3小时,采用两种UV-B剂量(CIE加权为每天每平方米2.8或5.4千焦)或仅用可见光照射。这些UV-B剂量分别相当于芬兰5月初太阳UV-B自然最大日剂量略低于环境水平以及增加80%的情况。单独的UV-B辐射仅使死亡率略有增加(分别为2.7%和4.0%)。同样,单独的惹烯未导致死亡率。相反,同时暴露于UV-B和惹烯会使白鲑死亡率极高,在最高惹烯浓度下所有幼体均死亡。惹烯的光诱导急性半数致死浓度(LC50)为13.3微克/升。经惹烯处理的鱼类在暴露于紫外线期间及之后表现出行为刺激和缺氧迹象。在同时暴露于惹烯和UV-B的幼体中检测到严重的皮肤损伤。在UV-B及溶剂对照(二甲基亚砜)加UV-B处理组中也能看到晒伤的结构迹象。即使在最低惹烯浓度下,同时进行化学和UV-B处理时黏液细胞数量也显著增加。我们认为这种组织反应是针对紫外线诱导的惹烯毒性的一种保护反应。此外,关于肝实质,暴露于UV-B和惹烯的鱼类出现病变,显示出肝毒性。我们建议,UV-B辐射与诸如惹烯等光活化污染物的协同作用是受纸浆和造纸工业化学污染的湖泊区域中需要考虑的一个潜在风险因素。