纳米二氧化钛致日本青鳉鱼胚胎毒性效应特征
Toxic effects of nanometer titanium dioxide on embryos of Japanese medaka(Oryzias latipes)
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摘要: 采用青鳉鱼胚胎暴露的方法,研究不同浓度纳米TiO2对胚胎的毒性效应.结果表明,纳米TiO2 24 h的半数致死率LD50为115.17 mg·L-1,但不同浓度组引起致死效应差别很大,不存在剂量—效应关系.随着处理浓度从高到低的变化,青鳉鱼胚胎孵化率呈现V字型降低.孵化率最低的为0.1 mg·L-1纳米TiO2处理组,其孵化率低于10%.高浓度组纳米TiO2(1 mg·L-1试验组和10 mg·L-1试验组)导致青鳉鱼胚胎孵化时间延迟1—2周.高浓度组(1 mg·L-1和10 mg·L-1处理组)和低浓度组(0.1 mg·L-1和0.01 mg·L-1处理组)的纳米TiO2对青鳉鱼胚胎和幼鱼造成的畸形毒性特征不同.高浓度组主要造成卵黄囊水肿,低浓度组的毒性特征主要是卵膜破损和胚胎急性致死.对纳米TiO2的致毒机理,尤其是低于0.1mg·L-1的毒性效应和致毒机理需要进一步研究.Abstract: In this study, we investigated the toxic effects of nano-TiO2 on embryos of the Medaka fish (Oryzias latipes) at different exposure concentrations of nano-TiO2. The results showed that the LD50 (Lethal Dose, 50%) of nano-TiO2 at 24 h was 115.17 mg·L-1. However, the lethal effects of Medaka embryos varied greatly among different concentration groups, and no dose-effect correlation can be observed. The hatching rate of Medaka embryos was no more than 10% and changed as ″V″ pattern with the increasing TiO2 concentrations. The lowest hatching point was found in the treatment group of 0.1 mg·L-1 nano-TiO2. The hatching time of Medaka embryos was delayed for 1-2 weeks in the groups treated by higher exposure concentrations (1 mg·L-1 or 10 mg·L-1). Malformations of Medaka embryos were observed in all treatment groups. The abnormal characteristic of Medaka embryos and juvenile fish was different between low concentration groups (0.1 mg·L-1 and 0.01 mg·L-1) and high concentration groups (1 mg·L-1 and 10 mg·L-1). The treatment groups with high concentrations of nano-TiO2 caused edema of yolk sac of Medaka embryos, while those with low concentrations led to membrane rupture of eggs, part of which was broken and suffered acute lethality. Therefore, the variation of toxicities of nano-TiO2 towards Medaka embryos can be attributed to different exposure concentrations of nanomaterials. Further studies with lower exposure concentrations (-1) are needed to better understand the toxic mechanism of nano-TiO2 to aquatic organisms.
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Key words:
- nano-TiO2 /
- Medaka /
- embryo toxicity /
- malformations
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[1] U.S. Environmental Protection Agency. 2010. National case studies:Nanoscale titanium dioxide in water treatment and in topical sunscreen[S]. EPA/600/R-09/057F.Washington, DC. [2] HASHIMOTO K, IRIE H, FUJISHIMA A, et al. TiO2 photocatalysis:A historical overview and future prospects[J]. Journal of Applied Physics, 2005.44:8269-8285. [3] 侯东颖,冯佳,谢树莲,等.纳米二氧化钛胁迫对普生轮藻的毒性效应[J]. 环境科学学报,2012, 32(6):1481-1486. HOU D Y, FENG J, XIE S L, et al. Toxic effects of nanoparticle TiO2 stress on Chara vulgaris L.[J]. Acta Scientiae Circumstantiae, 2012, 32(6):1481-1486(in Chinese).
[4] 刘文婧,景传勇. 纳米二氧化钛光催化转化甲基砷的研究[J]. 环境科学学报,2016, 36(1):172-177. LIU W J, JING C Y, et al. Photocatalytic transformation of dimethylarsinicand monomethylarsonic acids by NanoTiO2[J]. Acta Scientiae Circumstantiae, 2016, 36(1):172-177(in Chinese).
[5] CHEN Z, MENG H, XING G M, et al. Acute toxicological effects of copper nanoparticles in vivo[J]. Toxicology Letters. 2006, 163:109-120. [6] RICHARD D, HANDY R O, EUGENIA V J, et al. The ecotoxicology of nanoparticles and nanomaterials:Current status, knowledge gaps, challenges, and future need[J]. Ecotoxicology, 2008, 17:315-325. [7] WANG B, FENG W Y, WANG T C, et al. Acute toxicity of nano-and micro-scale zinc powder in healthy adult mice[J]. Toxicology Letters, 2006, 161:115-123. [8] 王文斌. 纳米二氧化钛对大鼠中枢神经系统的影响及作用机制探讨[D].济南:山东大学,2014. WANG W B. Effect of nano titanium dioxide on the central nervous system in rats and the mechanism[D].Jinan:Shandong University, 2014(in Chinese). [9] 刘慧婷. 纳米二氧化钛引发小鼠肝脏损伤及其分子机制的研究[D].苏州:苏州大学,2014. LIU H T. Liver injury in mice caused by nano titanium dioxide and its molecular mechanism[D]. Suzhou:Soochow University, 2014(in Chinese). [10] BERMUDEZ E, MANGUM J B, ASGHARIAN B, et al. Long-term pulmonary responses of three laboratory rodent species to subchronic inhalation of pigmentary titanium dioxide particles[J]. Toxicological Sciences, 2002, 70:86-97. [11] GRIFFITT R J, HYNDMAN K, DENSLOW N D, et al. Sources fate and effects of engineered nanomaterials in the aquatic environment[J]. Toxicological Sciences, 2009, 107:404-412. [12] FEDERICI G, SHAW B J, HANDY R D, et al. Toxicity of titanium dioxide nanoparticles to rainbow trout (Oncorhynchus mykiss):Gill injury, oxidative stress, and other physiological effects[J]. Aquatic Toxicology, 2007, 84:415-430. [13] 伍辛泷,黄乾生,方超,等. 新兴海洋生态毒理学模式生物——海洋青鳉鱼(Oryzias melastigma)[J]. 生态毒理学报,2012, 7(4):345-353. WU X L, HUANG Q S, FANG C, et al. Oryzias melastigma:A New promising model organism for marine ecotoxicology[J]. Asian Journal of Ecotoxicology, 2012, 7(4):345-353(in Chinese).
[14] 查金苗,王子健. 利用日本青鳉早期发育阶段暴露评估排水的急、慢性毒性和内分泌干扰效应[J]. 环境科学学报,2005, 25(12):110-114. ZHA J M, WANG Z J. Assessment acute and chronic toxicity and endocrine disruption effects of whole effluent based on early stage development of Japanese medaka(Oryzias latipes)[J]. Acta Scientiae Circumstantiae, 2005, 25(12):110-114(in Chinese).
[15] SEYED-MOHAMMADREZA S, SHAHRAM R, BORIS J, et al. Efficacy of the hatching event in assessing the embryo toxicity of the nano-sized TiO2 particles in zebrafish:A comparison between two different classes of hatching-derived variables[J]. Ecotoxicology and Environmental Safety, 2015, 116:121-128. [16] MANSFIELDA C M, ALLOYA M M, HAMILTON J, et al. Photo-induced toxicity of titanium dioxide nanoparticles to Daphnia magna under natural sunlight[J]. Chemosphere,2015, 120:206-210. [17] MA H B, AMANDA B, STEPHEN A D, et al. Photo toxicity of TiO2 nano particles under solar radiation to two aquatic species:Daphnia Magna and Japanese Medaka[J]. Environmental Toxicology and Chemistry,2012, 31(7):1621-1629. [18] 辛元元. 纳米二氧化钛的水生生物毒理效应研究[D].杭州:浙江工业大学,2012. XIN Y Y. Study on aquatic biological toxicology of titanium dioxide nanoparticles[D].Hangzhou:Zhejiang University of Technology, 2012(in Chinese). [19] 刘世光. 纳米二氧化钛在水中的聚集沉积特性研究[D].哈尔滨:哈尔滨工业大学,2013. LIU S G. Study on aggregation and deposition characteristics of titanium dioxide nanoparticles in aqueous systems[D]. Harbin:Harbin Institute of Technology, 2013(in China). [20] ZHANG R, NIU Y J, LI Y W, et al. Acute toxicity study of the interaction between titanium dioxide nanoparticles and lead acetate in mice[J]. Environmental Toxicology and Pharmacology, 2010, 30(1):52-60. [21] PARK J H, KIM S, BARD A J. Novel carbon-doped TiO2 nanotube arrays with high aspect ratios for efficient solar water splitting[J]. Nano Lett, 2006, 6, 24-28. [22] CHENG J, FLAHAUT E, CHENG S H, et al. Effect of carbon nanotubes on developing zebrafish (Danio rerio) embryos[J]. Environmental Toxicology and Chemistry,2007, 26, 708-716. [23] KASHIWADA S. Distribution of nanoparticles in the see-through medaka (Oryzias latipes)[J]. Environmental Health Perspectives, 2006, 114(11):1697-1702. [24] 任文娟,汪贞,王蕾,等. 双酚A及其类似物对斑马鱼胚胎及幼鱼的毒性效应[J]. 生态毒理学报,2017,12(1):184-192. REN W J, WANG Z,WANG L, et al. Effects of bisphenol a and its analogues on zebrafish embryos and larvae[J]. Asian Journal of Ecotoxicology, 2017, 12(1):184-192(in Chinese).
[25] 杜青平,刘伍香,袁保红,等. 1,2,4-三氯苯对斑马鱼生殖和胚胎发育毒性效应[J]. 中国环境科学,2012,32(4):736-741. DU Q P, LIU W X, YUAN B H, et al. Reproduction and embryonic development toxicity of 1,2,4-TCB on zebrafish embryos[J]. China Environmental Science, 2012, 32(4):736-741(in Chinese).
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