School of Public Health, Seoul National University, Seoul 151-742, Republic of Korea.
Department of Health, Environment and Safety, Eulji University, Seongnam 461-713, Republic of Korea.
Aquat Toxicol. 2014 Oct;155:244-52. doi: 10.1016/j.aquatox.2014.07.004. Epub 2014 Jul 12.
Benzophenone-3 (BP-3) has been widely used in sunscreens and cosmetics to protect human skin from the harmful effects of UV irradiation. While BP-3 has been frequently detected in surface waters, sediments and biota, only limited information is available on its in vivo toxicity, particularly in fish. In the present study the endocrine disrupting capacity of BP-3 and its underlying mechanisms were investigated using Japanese medaka (Oryzias latipes). Adult Japanese medaka pairs (F0) were exposed to 0, 4.7, 8.4, 26, or 90 μg/L (or 0, 15, 50, 150, or 500 μg/L of BP-3 based on nominal concentration) for 14 d and its effects on sex steroid hormones, and transcription of various associated genes were determined. Following additional 14 d of exposure, the F1 eggs reproduced were counted and were further exposed to 0, 5.4, 12, or 30 μg/L of BP-3 (or 0, 15, 50, or 150 μg/L based on nominal concentrations) until 30 d after hatching. Chemical analysis of the exposed media confirmed transformation of BP-3 to benzophenone-1 (BP-1), a more potent estrogen agonist. After 14 d of the adult fish exposure, plasma concentrations of testosterone (T) significantly increased in male fish. The 17β-estradiol (E2) to T (E2/T) ratio showed significant decreases in both male and female fish. Overall down-regulation of gonadal steroidogenic genes such as star, cyp11a, cyp17, hsd3b, hsd17b3, and cyp19a was also observed. After 28 d of exposure, the daily average egg reproduction per female was significantly reduced at 26 μg/L of BP-3. However, hatchability of F1 eggs was not affected by continuous exposure. After continued exposure until 30 dph, juvenile fish showed concentration-dependent decrease of condition factor, but mortality was not affected. Our observation clearly indicates that endocrine balance and reproduction performance in fish could be affected by μg/L level exposure to BP-3. Consequences of longer term exposure over multi-generations warrant further investigation.
二苯甲酮-3(BP-3)已广泛应用于防晒霜和化妆品中,以保护人类皮肤免受紫外线照射的有害影响。虽然 BP-3 已在地表水、沉积物和生物群中频繁检出,但关于其体内毒性的信息有限,特别是在鱼类中。本研究采用日本青鳉(Oryzias latipes)研究了 BP-3 的内分泌干扰能力及其潜在机制。成年日本青鳉对(F0)暴露于 0、4.7、8.4、26 或 90μg/L(或基于名义浓度的 0、15、50、150 或 500μg/L 的 BP-3)下 14d,测定其对性激素和相关基因转录的影响。在额外暴露 14d 后,计数 F1 卵的繁殖数量,并进一步暴露于 0、5.4、12 或 30μg/L 的 BP-3(或基于名义浓度的 0、15、50 或 150μg/L 的 BP-3)直到孵化后 30d。暴露介质的化学分析证实 BP-3 转化为更有效的雌激素激动剂二苯甲酮-1(BP-1)。在成年鱼类暴露 14d 后,雄性鱼类血浆中睾丸酮(T)浓度显著升高。雌雄鱼的 17β-雌二醇(E2)与 T(E2/T)比值均显著降低。星、cyp11a、cyp17、hsd3b、hsd17b3 和 cyp19a 等性腺类固醇生成基因也出现总体下调。暴露 28d 后,BP-3 浓度为 26μg/L 时,雌鱼的平均日产卵数显著减少。然而,F1 卵的孵化率不受连续暴露的影响。继续暴露至 30dph 时,幼鱼的体况因子呈浓度依赖性下降,但死亡率不受影响。我们的观察结果清楚地表明,鱼类的内分泌平衡和繁殖性能可能会受到 BP-3μg/L 水平暴露的影响。在多代中进行更长时间暴露的后果值得进一步研究。