以短暂暴露于邻苯二甲酸二丙酯(Dipropyl Phthalate)之淡水多齿新米虾(Neocaridina denticulata)建立生态毒理基因组生物标志物
Development of Ecotoxicogenomic Biomarkers on the Freshwater Shrimp (Neocaridina denticulate) Following Short-Term Exposure to Dipropyl Phthalate
摘要: 邻苯二甲酸酯类化合物(phthalate esters; PAEs)是广泛用于塑料制品之塑化剂和造成环境污染甚为可观的內分泌干擾物質。本研究以多齿新米虾(Neocaridina denticulata)暴露于次致死剂量(50 mg/L)之一種PAE——邻苯二甲酸二丙酯(dipropyl phthalate; DPrP)1天,利用抑制性扣减杂交法建立一套基因组指标,探讨其全面基因的表现变化。实验中共筛得71个独特的表达序列标签(expressed sequence tages; ESTs),包括23ESTs对应为已知功能基因及48ESTs为未知功能。根据生理功能,已知功能基因分别与9类相关,包括代谢、呼吸、防御、核糖体、染色体、转译、传讯、视觉与结构。虾子暴露于高浓度DPrP (50 mg/L)时,3个免疫及代谢相关的基因和3个未知功能基因,共6个基因的mRNA表现量明显下降。暴露于非致死剂量1.0 mg/L时,共8个基因受到影响,包括正调节的4个已知功能和1个未知功能基因,以及3未知功能基因被负调控。虾子暴露于更低剂量0.5 mg/L后,仅4个基因受到影响,包括3个已知功能和1个未知功能基因之mRNA表现量明显上升。综合这些结果暗示,包括DPrP在內之非致死浓度PAEs污染的水域可能藉由影响多齿新米虾的生理功能而威胁其存活;此外,起源自多齿新米虾的ESTs也许可用在水生环境中其他污染物之生态毒性效应的研究。 Phthalate esters (PAEs), which are widely used in industrial chemicals that serve as important additives to impart flexibility to polyvinyl chloride resins and have become widely diffused in the environment, are considered to be endocrine disrupting chemicals (EDCs). In order to assess the toxicity of PAE to aquatic crustacean, after shrimps (Neocaridina denticulate) were short-term exposed to a sublethal concentration (50 mg/L) of dipropyl phthalate (DPrP), the differential expression genes were isolated and identified using suppression subtractive hybridization (SSH) on the samples prepared from the whole individual. There were 71 unique expressed sequence tags (ESTs) which were identified by homology with data-based sequences, including 23 ESTs corresponded to known genes and 48 ESTs with unknown function. The known genes could be divided into nine classes on the basis of physiological function: genes related to ribosomal, metabolism, immune and structural molecules, concerning the translation-related molecules, involved respiration and signaling, and responding to signaling and vision. By comparing the level of gene transcription in DPrP-treated group vs. non-treated group using semi-quantitative RT-PCR, we found that six of twelve selected genes were significantly up-regulated following exposure to DPrP at high concentration (50 mg/L), including two immune-related genes, one metabolism-related gene and 3 unknown genes. There were eight genes which are significantly responding to DPrP treatment at 1.0 mg/L, including five up-regulated genes (four known genes and one unknown gene) and three down-regulated unknown genes. After exposure to 0.5 mg/L of DPrP, only four genes (three known genes and one unknown gene) were affected and their mRNA levels increased significantly. These results suggest that N. denticulate may be harmed via the change of the globally physiological function following exposure in non-lethal PAE-polluted aquatic environment; in addition, the ESTs derived from N. denticulate can be used for studying the ecotoxicological effect of other pollutants in the aquatic environment.
文章引用:蔡伊茜, 宋宏红. 以短暂暴露于邻苯二甲酸二丙酯(Dipropyl Phthalate)之淡水多齿新米虾(Neocaridina denticulata)建立生态毒理基因组生物标志物[J]. 世界生态学, 2013, 2(4): 38-49. http://dx.doi.org/10.12677/IJE.2013.24007

参考文献

[1] Holmes, P., Harrison, P., Bergman, A., Brouwer, I., Brouwer, B., Keiding, N., Randall, G., Sharpe, R., Skakkebaek, N., Ashby, J., Barlow, S., Dickerson, R., Humfrey, C. and Smith, L.M. (1997) European workshop on the impact of endocrine disrupters on human and wildlife. Proceedings of a Workshop, Weybridge, UK, Report NO. EUR 17549.
[2] Staples, C.A., Peterson, D.R., Parkerton, T.F. and Adams, W.J. (1997) The environmental fate of phthalate esters: A literature review. Chemosphere, 35, 667-749.
[3] Yin, M.C. and Su, K.H. (1996) Investigation on risk of phthalate ester in drinking water and marketed foods. Journal of Food and Drug Analysis, 4, 313-318.
[4] Liu, C., Wang, S.K. and Lu, Y.B. (2000) Chemical characteriza- tion of Tamshui River sediment in northern Taiwan. Journal of Food and Drug Analysis, 76, 205-218.
[5] Chang, B.V., Liao, C.S., Huang, B.B. and Lee, C.C. (2004) Occurrence of phthalate esters in Taiwan. Proceeding of the Third Conference on Environmental Hormones and POPs, Tai- pei, 12 November 2004, 63-66.
[6] Eckardt, R.E. (1973) Recent developments in industrial car- cinogens. Journal of Occupational Medicine, 15, 904-907.
[7] Tavares, I.A. and Vine, N.D. (1985) Phthalic acid esters inhibit arachidonate metabolism by rat peritoneal leucocytes. Journal of Pharmacy and Pharmacology, 37, 67-68.
[8] Carozzi, S., Nasini, M.G., Schelotto, C., Caviglia, P.M., Santoni, O. and Pietrucci, A. (1993) A biocompatibility study on perito- neal dialysis solution bags for CAPD. Advances in Peritoneal Dialysis, 9, 138-142.
[9] Jha, A.M., Singh, A.C. and Bharti, M. (1998) Germ cell muta- genicity of phthalic acid in mice. Mutation Research, 422, 207- 212.
[10] Autian, J. (1973) Toxicity and health threats of phthalate esters: Review of the literature. Environmental Health Perspectives, 4, 3-26.
[11] Thomas, J. and William, L. (1975) Biodegradation of di-n-butyl phthalate and di-2-ethylhexyl phthalate in freshwater hydrosoil. Journal of Fisheries Science and Technology, 32, 333-339.
[12] Capacchietti, M., Sabbieti, M.G., Materazzi, S., Materazzi, G., Menghi, G. and Marchetti, L. (2007) Phthalate esters immu- nolocalized in the gastrointestinal tract of shi drum, Umbrina cirrosa (L.) and rainbow trout, Oncorhynchus mykiss (W.). His- tology and Histopathology, 22, 15-21.
[13] Norman, A., Borjeson, H., David, F., Tienpont, B. and Norrgren, L. (2007) Studies of uptake, elimination, and late effects in At- lantic salmon (Salmo salar) dietary exposed ot di-2-ethylhexyl phthalate (DEHP) during early life. Archives of Environmental Contamination and Toxicology, 52, 235-242.
[14] Schweer, L.G. (2002) Draft detailed review paper on mysid life cycle toxicity test. US Environmental Protection Agency, Wash- ington DC.
[15] Shigehisa, H. and Shiraishi, H. (1998) Biomonitoring with shrimp to detect seasonal change in river water toxicity. Envi- ronmental Toxicology and Chemistry, 17, 687-694.
[16] Fossi, M.C., Marsili, L., Neri, G., Casini, S., Bearzi, G., Politi, F., Zanardelli, M. and Panigada, S. (2000) Skin biopsy of mediter- ranean cetaceans for the investigation of interspecies suscepti- bility to xenobiotic contaminants. Marine Environmental Re- search, 50, 517-521.
[17] Kirkpatrick, A.J., Gerhardt, A., Dick, J.T.A., McKenna, M. and Berges, J.A. (2006) Use of the multispecies freshwater biomonitor to assess behavioral changes of Corophium volutator (Pallas, 1766) (Crustacea, Amphipoda) in response to toxicant exposure in sediment. Ecotoxicology and Environmental Safety, 64, 298- 303.
[18] Kitamura, H. (1990) Relation between the toxicity of some toxicants to the aquatic animals (Tanichthys albonubes and Neocaridina denticulata) and the hardness of the test. Bulletin of the Faculty of Fisheries Nagasaki University, 67, 13-19.
[19] Huang, D.J. and Chen, H.C. (2004) Effects of chlordane and lindane on testosterone and vitellogenin levels in green neon shrimp (Neocaridina denticulate). International Journal of Toxi- cology, 23, 91-95.
[20] Huang, D.J., Chen, H.C., Wu, J.P. and Wang, S.Y. (2006) Re- production obstacles for the female green neon shrimp (Neo- caridina denticulate) after exposure to chlordane and lindane. Chemosphere, 64, 11-16.
[21] Sung, H.H., Lin, Y.H. and Hsiao, C.Y. (2011) Potential toxicity of dipropyl phthalate to physiological functions of the green neon shrimp (Neocaridina denticulate). Fish & Shellfish Immu- nology, 31, 511-515.
[22] Larkin, P., Knoebl, I. and Denslow, N.D. (2003) Differential gene expression analysis in fish exposed to endocrine disrupting compounds. Comparative Biochemistry and Physiology Part B: Biochemistry and Molecular Biology, 136, 149-161.
[23] Sung, H.H., Kao, W.Y. and Su, Y.J. (2003) Effects and toxicity of phthalate esters to hemocytes of giant frechwater prawn, Macrobranchium rosenbergii. Aquatic Toxicology, 64, 25-37.
[24] Lu, K.Y., Huang, Y.T., Lee, H.H. and Sung, H.H. (2006) Cloning the prophenoloxidase cDNA and monitoring the expression of proPO mRNA in prawns (Macrobrachium rosenbergii) stimu- lated in vivo by CpG oligodeoxynucleotides. Fish & Shellfish Immunology, 20, 274-284.
[25] Liu, C.L. and Sung, H.H. (2011) Genes are differentially ex- pressed at transcriptional level of Neocaridina denticulata fol- lowing short-term exposure to nonylphenol. Bulletin of Envi- ronmental Contamination and Toxicology, 87, 220-225.
[26] Feng, L., Miao, W. and Wu, Y. (2007) Differentially expressed genes of Tetrahymena thermophila in response to tributyltin (TBT) identified by suppression subtractive hybridization and real time quantitative PCR. Aquatic Toxicology, 81, 99-105.
[27] Victor, B., Narayanan, M. and JonesNelson, D. (1990) Gill pa- thology and hemocyte response in mercury exposed Macro- brachium idae (Heller). Journal of Environmental Biology, 11, 61-65.
[28] Sindermann, C.J. (1979) Pollution-associated diseases and ab- normalities of fish and shellfish: A review. Fishery Bulletin, 76, 717-749.
[29] Van Holde, K., Miller, K.I. and Decker, H. (2001) Hemocyanin and invertebrate evolution. The Journal of Biological Chemistry, 276, 15563-15566.
[30] Rainer, J. and Brouwer, M. (1993) Hemocyanin synthesis in the blue crab Callinectes sapidus. Comparative Biochemistry and Physiology, 104, 69-73.
[31] Decker, H. and Rimk, T. (1998) Two different functions of one active site: Binding oxygen and phenoloxidase activity of hemo- cyanin of tarantula hemocyanin. The Journal of Biological Che- mistry, 273, 25889-25892.
[32] Decker, H. and Tuczek, F. (2000) Phenoloxidase activity of hemocyanins: Activation, substrate orientation and molecular mechanism. Trends in Biochemical Sciences, 25, 392-397.
[33] Decker, H. and Terwilliger, N. (2000) Cops and robbers: Putative evolution of copper oxygen-binding proteins. The Journal of Experimental Biology, 203, 1777-1782.
[34] Decker, H., Ryan, M., Jaenicke, E. and Terwilliger, N. (2001) SDS-induced phenoloxidase activity of hemocyanins from Limulus polyphemus, Eurypelma californicum, and Cancer ma- gister. The Journal of Biological Chemistry, 276, 17796-17799.
[35] Nagai, T. and Kawabata, S.I. (2000) A Link between blood co- agulation and prophenoloxidase activation in arthropod host de- fense. The Journal of Biological Chemistry, 275, 29264-29267.
[36] Nagai, T., Osaki, T. and Kawabata, S. (2001) Functional conver- sion of hemocyanin to phenoloxidase by horseshoe crab antim- icrobial peptides. The Journal of Biological Chemistry, 276, 27166-27170.
[37] Destoumieux-Garzon, D., Saulnier, D., Garnier, J., Jouffery, C., Bulet, P. and Bachère, E. (2001) Crustacean immunity. Antifun- gal peptides are generated from the C terminus of shrimp hemocyanin in response to microbial challenge. The Journal of Biological Chemistry, 276, 47070-47077.
[38] Loftus, T.M., Nguyen, Y.H. and Stanbridge, E.J. (1997) The QM protein associates with ribosomes in the rough endoplasmic re- ticulum. Biochemistry, 36, 8224-8230.
[39] Dick, F.A., Karamanou, S. and Trumpower, B.L. (1997) QSR1, an essential yeast gene with a genetic relationship to a subunit of the mitochondrial cytochrome bc1 complex, codes for a 60 S ri- bosomal subunit protein. The Journal of Biological Chemistry, 272, 13372-13379.
[40] Marty, I., Brugidou, C., Chartier, Y. and Meyer, Y. (1993) Growth-related gene expression in Nicotiana tabacum mesophyll protoplasts. The Plant Journal, 4, 265-278.
[41] Green, H., Canfield, A.E., Hillarby, M.C., Grant, M.E., Boot- Handford, R.P., et al. (2000) The ribosomal protein QM is ex- pressed differentially during vertebrate endochondral bone de- velopment. Journal of Bone and Mineral Research, 5, 1066- 1075.
[42] Xu, J., Wu, S. and Zhang, X. (2008) Novel function of QM protein of shrimp (Penaeus japonicus) in regulation of phenol- loxidase activity by interaction with hemocyanin. Cellular Physiology and Biochemistry, 21, 473-480.
[43] Fagotto, F. (1990) Yolk degradation in tick eggs. II. Evidence that cathepsin L-like proteinase is stored as a latent, acid-acti- vable proenzyme. Archives of Insect Biochemistry and Physiol- ogy, 14, 237-252.
[44] Homma, K., Kurata, S. and Natori, S. (1994) Purification, char- acterization, and cDNA cloning of procathepsin L from the cul- ture medium of NIH-Sape-4, an embryonic cell line of Sarco- phaga peregrina (flesh fly), and its involvement in the differen- tiation of imaginal discs. The Journal of Biological Chemistry, 269, 15258-15264.
[45] Matsumoto, I., Watanabe, H., Abe, K., Arai, S. and Emori, Y. (1995) A putative digestive cysteine proteinase from Drosophila melanogaster is predominantly expressed in the embryonic and larval midgut. European Journal of Biochemistry, 227, 582-587.
[46] Warner, A.H. and Matheson, C. (1998) Release of proteases from larvae of the brine shrimp Artemia franciscana and their potential role during the molting process. Comparative Bio- chemistry and Physiology Part B: Biochemistry and Molecular Biology, 119, 255-263.
[47] Hashmi, S., Britton, C., Lie, J., Guiliano, D.B., Oksov, Y. and Lustigman, S. (2002) Cathepsin L is essential for embryogenesis and development of Caenorhabditis elegans. The Journal of Biological Chemistry, 277, 3477-3486.
[48] Tobin, D.J., Foitzik, K., Reinbeckel, T., Mecklenburg, L., Bot- chkarev, F.A., Peters, C. and Paus, R. (2002) The lysosomal protease cathepsin L is an important regulator of keratinocyte and melanocyte differentiation during hair follicle morphogene- sis and cycling. The American Journal of Pathology, 16, 1807- 1821.
[49] Wood, A.W. and Van Der Kraat, G. (2003) Yolk proteolysis in rainbow trout oocytes after serum-free culture: Evidence for a novel biochemical mechanism of atresia in oviparous vertebrates. Molecular Reproduction and Development, 65, 219-227.
[50] Knop, M., Schiffer, H.H., Rupp, S. and Wolf, D.H. (1993) vacuolar/lysosomal proteolysis: Protease, substrates mechanisms. Current Opinion in Cell Biology, 5, 990-996.
[51] Le Boulay, C., Sellos, D. and Van Wormhoudt, A. (1998) Ca- thepsin L gene organization in crustaceans. Gene, 218, 77-84.
[52] Hu, K.J. and Leung, P.C. (2004) Shrimp cathepsin L encoded by an intronless gene has predominant expression in hepatopan- creas, and occurs in the nucleus of oocyte. Comparative Bio- chemistry and Physiology Part B: Biochemistry and Molecular Biology, 137, 21-33.
[53] Zhao, Z.Y., Yin, Z.X., Weng, S.P., Guan, H.J., Li, S.D., Ke, X., Chan, S.M. and He, J.G. (2007) Profiling of differentially ex- pressed genes in hepatopancreas of white spot syndrome virus- resistant shrimp (Litopenaeus vannamei) by suppression sub- tractive hybridization. Fish & Shellfish Immunology, 22, 520- 534.
[54] Ren, Q., Zhang, X.W., Sun, Y.D., Sun, S.S., Zhou, J., Wang, Z.H., Zhao, X.F. and Wang, J.X. (2010) Two cysteine pro-teinases respond to bacterial and WSSV challenge in Chinese white shrimp Fenneropenaeus chinensis. Fish & Shellfish Immunology, 29, 551-556.
[55] Li, W.W., Jin, X.K., He, L., Jiang, H., Gong, Y.N., Xie, Y.N. and Wang, Q. (2010) Molecular cloning, characterization, expression and activity analysis of cathepsin L in Chinese mitten crab, Eri- ocheir sinensis. Fish & Shellfish Immunology, 29, 1010-1018.
[56] Ma, J., Zhang, D., Jiang, J., Cui, S., Pu, H. and Jiang, S. (2010) Molecular characterization and expression analysis of cathepsin L1 cysteine protease from pearl oyster Pinctada fucata. Fish & Shellfish Immunology, 29, 501-507.