海南岛海域麻痹性贝毒和腹泻性贝毒的污染状况及其监测管理方案设计
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摘要
近年来海南岛海域赤潮频发,因食用贝类而引起的麻痹性贝毒(paralytic shellfishpoisoning,PSP)和腹泻性贝毒(diarrhetic shellfish poisoning,DSP)中毒事件时有发生,严重制约海南岛滨海旅游业和水产养殖业的发展并威胁人类的健康。为此,本研究于2010年冬季至2011年秋季间,在海南岛的文昌、澄迈、洋浦、陵水等5个海域采集了14种95份贝类样品,进行PSP和DSP检测,旨在获取PSP和DSP在海南岛沿海海域的分布特征。主要研究结果如下:
     1、海南岛海域PSP的污染状况
     ①海南岛沿海海域贝类中PSP的含量较低,最高检出毒力值为3.576Mu/g,检出率为11.58%。②海南岛沿海海域贝类中PSP的季节变化非常明显,以冬季最高,秋季次之,其他两季均未检出PSP。③海南岛沿海海域贝类中PSP的地理分布较广,除澄迈海域没有检出,文昌、洋浦等沿海贝类中均有PSP检出,其中陵水沿海海域贝类中PSP的检出率最高。④海南岛海域贝类中PSP的主要富集种为细纹卵蛤、织纹螺、翡翠贻贝和栉江珧。⑤共检出11种PSP成分,主要成分有GTX1、GTX4、C1、C2,高毒力值的NEO和STX含量较少,其它毒素成分如deGTX3,deGTX2,GTX3,GTX2和dcSTX的含量也十分低。
     2、海南岛海域DSP的污染状况
     ①海南岛海域贝类中的DSP检出率和超标率均比较高,分别达到46.32%和33.68%。在超标的贝类样品中,最高毒力值达0.2Mu/g。②海南岛海域贝类中DSP的污染状况在冬季最为严重,检出率和超标率均达到56.25%,夏季贝类中的DSP污染最小,贝类中DSP含量无超标情况。③海南岛海域贝类中DSP的分布范围较为广泛,在各个采样点均有检出,就地域分布而言,海南岛东、南部海域贝类中DSP的污染状况较西、北部严重。④此次在海南岛海域共调查了14种贝类,其中有11种贝类中检测出含有DSP,分别是裂纹格特蛤、华贵栉孔扇贝、魁蚶、栉江珧、方斑东风螺、波纹巴非蛤、文蛤、衣紫蛤、织纹螺、近江牡蛎和翡翠贻贝,其中污染状况较为严重有栉江珧、裂纹格特蛤、近江牡蛎、华贵栉孔扇贝和魁蚶。
     在此调查研究的基础上,本论文设计了海南岛沿海海域的贝毒监测和管理方案,为相关部门在贝类赤潮毒素管理方面提供理论参考。
The red tides broke out frequently and the seafood poisoning cases of paralytic shellfishpoisoning (PSP) and diarrhetic shellfish poisoning (DSP) caused by edible shellfish oftenoccured in the area around Hainan island, which restrict the development of seaside tourism andaquaculture and threaten human health. To understand the pattern and toxin profiles of PSP andDSP in the coastal waters of Hainan island, an investigation was carried out and fourteenshellfish species and95shellfish samples were collected in the sea areas of Wenchang,Chengmai, Yangpu, Lingshui and Dongfang from the winter of2010to the spring of2011. Themain results are as follows:
     1, Contaminated characteristics of PSP in Hainan island and its adjacent sea areas
     ①The risk of PSP toxins pollution was lower in Hainan island and its adjacent sea areas,the maximum content of PSP was3.576Mu/g, the positive rates of PSP was11.58%.②Thepositive rates of PSP showed a markedly seasonal differentiation,the rates reached the highest inwinter,took second place in autumn,and there was no positive case in other two seasons.③Thegeographical distribution of PSP was widely spread, PSP was detected in many sea areas exceptthe adjacent sea areas of Chengmai, the maximum positive rate of PSP was in the adjacent seaareas of Lingshui.④The shellfish species that were subjected to accumulate PSP included Pitarstriata、 Nassarius coronatus、 Perna viridis and Atrina pectinata.⑤There were elevencomponents of PSP in the samples, GTX1、GTX4、C1and C2were the principal profiles,the highpotency toxins (NEO and STX) had a low proportion, the content of other toxins such asdeGTX3,deGTX2,GTX3,GTX2and dcSTX was also very low.
     2, Contaminated characteristics of DSP in Hainan island and its adjacent sea areas
     ①The risk of DSP toxins pollution were higher in Hainan island and its adjacent sea areas,and the positive rate and over-standard rate of DSP were46.32%and33.68%out of the totalsamples respectively, the maximum content of DSP is0.2Mu/g.②The pollution of DSP in winteris the most serious, both the positive rate and the over-standard rate of samples were reached56.25%, and the lowest in summer, there was no over-standard case in this season.③Thegeographical distribution of DSP was widely spread, the pollution of DSP in the east and southof Hainan island was more serious than the west and north.④There were14shellfish species inthis investigation,the species that were subjected to contaminate DSP included Marcia hiantina、Chlamys nobilis、Scapharca broughtoni、Atrina pectinata、Babylonia areolata、Paphia undulate、 Meretrix meretrix、Psammotaena togata、Nassarius coronatus、Crassostrea rivularis and Pernaviridis, among these species, the most susceptible species were Atrina pectinata、Marciahiantina、Crassostrea rivularis、Chlamys nobilis and Scapharca broughtoni.
     on the basis of the investigation, the biotoxin monitoring and management program in thearea of Hainan island and its adjacent sea area was proposed, in order to mitigate the risk ofshellfish toxins.
引文
[1]Leigh L. A review of Paralytic Shellfish Poisoning.National Office of Animal andPlant Health Agriculture,Fisheries and Forestry-Australia Canberra.2000.
    [2]Karsten R, Justus E. E.van B. Interactive effects of global and regional change on acoastal ecosystem. Helgol Mar Res,2008,62:85-91.
    [3]江天久,陈菊芳,邹迎麟.中国东海和南海有害赤潮高发区麻痹性贝毒素研究[J].应用生态学报.2003,14(7):1156-1160.
    [4]王红勇,唐天乐,黄飞.海南省赤潮状况及防治对策[J].中国水产,2010,1:66-67.
    [5]杨美兰,贾晓平,林钦.南海海域重要养殖水域牡蛎体中的腹泻性贝类毒素[J].海洋环境科学,2009,28(4):410-413.
    [6]吴施卫,卢楚谦,刘景钦.海南省近岸海域麻痹性贝毒素分析[J].海洋环境科学,2006,25(1):27-29.
    [7]Francesco P, Michelle C M, Rosalia C. Evidence for differences in the metabolismof saxitoxin and C1+2toxins in the freshwater cyanobacteriumCylindrospermopsis raciborskii T3.Biochimica et Biophysica Acta.2004,1674:60-67.
    [8]Pereira P, Onodera H, Andrinolo D. Paralytic shellfish toxins in the freshwatercyanobacterium Aphanizomenon flos-aquae isolated from Montargil reservoir,Portugal. Toxicon.2000,38(12):1689-1702.
    [9]Paulo P, Elsa D, Stephan P. Accumulation of paralytic shellfish toxins (PST) fromthe cyanobacterium Aphanizomenon issatschenkoi by the cladoceran Daphniamagna.Toxicon.2004,44:773-780.
    [10]Wang Z H, Matsuoka K, Qi Y Z. Dinoflagellate cysts in recent sediments fromChinese coastal waters.Marine Ecology.2004,25(4):289.
    [11]Kazumi M,Linda B J,Yuichi K. Modern dinoflagellate cysts in hypertrophiccoastal waters of Tokyo Bay,Japan.Plankton Research,2003,25(12):1461-1470.
    [12]Gallacher S, Flynn K J, Franco J M.Evidence for production of paralytic shellfishtoxins by bacteria associated with Alexandrium spp.(Dinophyta) in culture. ApplEnviron Microbiol.1997,63:239-245.
    [13]Michaud S, Levasseur M, Doucette G. Particle size fractionation of paralyticshellfish toxins (PSTS):seasonal distribution and bacterial production in the StLawrence estuary, Canada. Toxicon.2002,40:1451-1462.
    [14]Harmful Algae.Distribution of HABs throughout the World. http://www. whoi.edu/redtide/page.do?pid=14899.
    [15]Gessner B, Middaugh J. Paralytic shellfish poisoning in Alaska: a20-yearretrospectiveanalysis. Am J Epidemiol.1995,141:766-770.
    [16]Mata L, Abarca G, Marranghello L. Intoxicacion paralitica por mariscos (IPM)porSpondylus calcifer contaminado con Pyrodinium bahamense, Costa Rica,1989-1990.Rve Biol Trop.1990,38:129-136.
    [17]Castaneda O S, Castellanos J V, Galvan J. Intoxicaciones protoxina paralizante demolusco en Oaxaca. Salud Pubica Mex.1991,33:240-247.
    [18]周名江,李钧,于仁诚.赤潮藻毒素研究进展[J].中国海洋药物,1999,71(3):48-54.
    [19]Mons M N, Van Egmond H P, Speijiers G J A.Paralytic shellfish poisoring:Areview.RIVM Report388802005.1998,6.
    [20]Baden, D G., Marine food-borne dinoflagellate toxins, International Review ofCylology, Academic Press, NewYork,1983,82:99-150.
    [21]Benton B J,Keller S A,Spriggs D L.Recovey from the lethal effects of saxitoxin:atherapeutie window for4-aminopyridine(4-AP). Toxicon.1998,36(4):571-588.
    [22]王焕玲,梁玉波,刘仁沿.我国麻痹性贝毒的研究现状[J].水产科学,2008,27(7):374-378.
    [23]GB18406.4-2001.农产品安全质量无公害水产品安全要求[S].
    [24]刘智勇,计融.各国贝类水产品中麻痹性贝类毒素限量标准的比对[J]中国热带医学,2006,6(1):176-178.
    [25]Chen C Y,Chou H N. Accumulation and depuration of paralytic shellfishpoisoning toxins by purple clam Hiatula rostrataLighttoot.Toxicon,2001,39:1029-1034.
    [26]Powell C L,Doucette G J. A receptor binding assay for paralytic shellfishpoisoning toxins: recent advances and applicatons. Nat Toxins,1999,7(6):393-400.
    [27]GB/T5009.213-2008贝类中麻痹性贝类毒素的测定[S].
    [28]Lee J S,tangen K,Yasumoto T. Diarrhetic shellfish toxins in Norwegianmussels.Nippon suisan gakkaishi.1988,54(11):1953-1957.
    [29]丁君.赤潮毒素中腹泻性贝毒和麻痹性贝毒的研究及进展[J].大连水产学院学报,2001,16(3):212-218.
    [30]赵晓芳,计融.腹泻性贝类毒素研究进展[J].中国热带医学,2006,6(1):157-159.
    [31]杨维东,刘喜春,刘洁生.腹泻性贝毒研究现状[J].海洋科学,2005,29(5):66-72.
    [32]陈则玲,付云娜,巩宁.腹泻性贝毒及其高效液相色谱检测方法[J].海洋通报,2000,19(1):73-78.
    [33]王菊英,关道明,韩庚辰.腹泻性贝类毒素的分析方法研究[J].海洋环境科学,1996,15(4):62-67.
    [34]Burgess V, Shaw G. Pectenotoxins-an issue for public health (A review of theircomparative toxicology and metabolism).Environment International,2001,27:275-283.
    [35] Satake M, MacKenzie L, Yasumoto T. Identification of Protoceratium reiculatumas the biogenetic orgin of yessotoxin. Nat Toxins1997,5:164-167.
    [36]钱宏林,梁松,齐雨藻.广东沿海赤潮的特点及成因研究[J].生态科学,2000,19(3):132-136.
    [37]李伟才,栾刚,李立.中国沿海部分海区贝毒毒素的调查[J].海洋科学,2000,24(6):156-163.
    [38]Shumway, Sandra E.A review of the effects of algal blooms on shellfish andaquaculture [J].Journal of The World Aquaculture Society,1990,21(2):65-104.
    [39]Morton S L, Tindall D R. Determination of okadaic acid content of dinoflagellatecells: a comparison of the HPLC-fluorescent method and two monoclonalantibody ELISA test kits. Toxicon,1996,34(8):947-954.
    [40]吴施卫,张纯超,卢楚谦.南海近岸海域腹泻性贝类毒素分析[J].海洋环境科学,2005,24(4):48-51.
    [41]Anderson D M,Anderson P, Bricelj V M. Rensel Monitoring and managementstrategies for harmful algal blooms in coastal waters. Asia Pacific EconomicProgram, Singapore, and International Oceanographic Commission TechnicalSeries.2001,5,105-152.
    [42] Association of Official Analytical Chemist(AOAC).Standard mouse bioassay forparalytic shellfish toxins[A].HORWITZ P.Official methods ofanalysis[C].Washington DC:Association of Official AnalyticChemists,1980,298-299.
    [43]OSHIMA Y.Post-column derivatization HPLC methods for paralytic shellfishpoisons[A]. Hallegraeff G,Anderson DM,Cembella AD.Manual on harmful marinemicroalgae [C].France:UNESCO’s Workshops,1995,81-94.
    [44]林燕棠,杨美兰,陈瑞雯.广东沿海麻痹性贝类毒素的研究[J].海洋与湖沼,1994,25(2):220-225.
    [45]Chen K Y. Occurrence of paralytic shellfish poison in finfish. Supplement to theJournal of Sun Yatsen Zlniversity,1995,3:18~23.
    [46]齐雨藻,吕颂辉.南海大鹏湾浮游植物的生态特征[J].暨南大学学报(自然科学版),1995,16(1):111-117.
    [47]朱白婢,陈宏,李春强.海南省红沙港海水中浮游植物现状调查[J].安徽农业科学,2007,35(2):484-485.
    [48]梁计林,龙丽娟,张偲.微量元素Fe、Mn、Co对有毒甲藻生长和产毒的影响[J].热带海洋学报,2011,30(1):119-123.
    [49]Anderson D M, Kuhs D M,Qi Y Z. Paralytic shellfish poisoning in SouthernChina.Toxicon.1996,34(5):579-590.
    [50]郑淑贞,林晓.麻痹性贝毒[J].广州化学,1995,2:39-43.
    [51]戴明,李纯厚,张汉华.海南岛以南海域浮游植物群落特征研究[J].生物多样性,2007,15(1):23-30.
    [52]林金美.南海中部浮游甲藻类的生态研究[J],海洋通报,1988,7(3):47-53.
    [53]林金美,张金标.江苏,浙江近岸海域浮游生的初步调查[J],海洋科技,1980,5(2):9-19.
    [54]吴施卫,卢楚谦,朱小山.广东沿海麻痹性贝毒素的地理分布特征[J].海洋环境科学.2005b,24(3):40-43.
    [55]江天久,江涛.中国沿海部分海域麻痹性贝毒研究[J].海洋与湖沼,2007,38(1):36-41.
    [56]Oshima Y, Yasumoto T, Kodama M. Features of paralytic shellfish poisoning inTohoku district. Bull. Jpn. Soc. Sci. Fish,1982,48:525-530.
    [57]刘智勇,李燕俊,江涛.麻痹性贝类毒素污染状况及检测方法的比对研究[J].中国热带医学,2010,10(11):1426-1428.
    [58]于仁成,周名江,李爱峰.中国沿海两例食用织纹螺中毒事件中织纹螺体内毒素分析[J].中国水产科学,2007,14(5):801-806.
    [59]张农,苏捷,刘海新,叶孙忠.我国东南沿海地区织纹螺科的种类与毒性[J].生态毒理学报,2009,2(4):289-294.
    [60]张树刚,刘亚林,陈雷.浙南海域麻痹性贝毒研究[J].海洋环境科学,2011,30(5):703-706.
    [61]宋普江,张伟,王刚.大连近岸海域经济贝类麻痹性贝毒分析[J].海洋环境科学,2011,30(4):532-535.
    [62]范放,李小燕.麻痹性贝类毒素监测指示贝种的筛选研究[J].中国食品卫生杂志,2006,18(6):542-544.
    [63]沈和定,付金花,冉福.麻痹性贝毒在文蛤体内的累积及净化技术研究[J].海洋科学,2011,35(7),45-50.
    [64]Abouabdellah R,Taleb H,Bennouna A.Paralytic shellfish poisoning toxin profileof mussels Perna perna from southern Atlantic coasts of Morocco. Toxicon.2008,51:780-786.
    [65]Taleb H,Vale P,Jaime E.Study of paralytic shellfish poisoning toxin profile inshellfish from the Mediterranean shore of Morocco.Toxicon.2001,39:1855-1861.
    [66]Taleb H,Vale P,Blaghen M.Spatial and temporal evolution of PSP toxins along theAtlantic shore of Morocco.Toxicon.2003,41:199-205.
    [67]邹迎麟,朱明远. HALL S.两种亚历山大藻产毒过程和毒素特征研究[J].黄渤海海洋,2001,19(3):65-70.
    [68]贺华,王学魁,孙之南.渤海裸甲藻和链状亚历山大藻的麻痹性贝毒毒素分析[J].海洋通报,2007,26(5):67-73.
    [69]梁计林,何伟宏,龙超.慢原甲藻—南海热带附生甲藻新记录[J].热带亚热带植物学报,2011,19(1):40-44.
    [70]齐雨藻,钱锋,郑磊.中国东南沿海赤潮的生理生态学研究[A].中国赤潮研究(SCOR-IOC赤潮工作组中国委员会第二次会议论文选)[C].青岛:青岛出版社,1996,6-16.
    [71] Oshima Y. Chemical and enzymatic transformation of paralytic shellfish toxins inmarine organisms[A]. Harmful Marine Algal Blooms[M],1995,475-480.
    [72]李春盛,刘宁.贝毒素的卫生危害和检测方法论[J].中国公共卫生学报.1998.17:373-376.
    [73]SN/T2131.2-2010腹泻性贝毒的小白鼠生物检测法[S].
    [74]张树刚,邹清,陈雷.浙南海腹泻性贝毒分析[J].海洋环境科学,2011,35(1):44-53.
    [75]徐志斌,吴施卫,陈凯彪.广东省近岸海域贝类腹泻性毒素含量与胃含物的分析[J].海洋通报,2010,29(4):444-449.
    [76]江天久,尹伊伟,骆育敏.大亚湾和大鹏湾麻痹性贝类毒素动态分析[J].海洋环境科学.2000,19(2):1-5.
    [77]Murakami Y, Oshima Y, Yasumoto T. Identification of okadaic acid as a toxiccomponent of a marine dinoflagellate Prorocentrum lima. Bull Jpn Soc SciFish,1982,48:69-72.
    [78] Campbell L, Olson R J, Sosk H M. First harmful Dinophysis (Dinophyceae,Dinophysiales) Bloom in the US is revealed by automated imaging flowCytometry. Journal of Phycolgy,2010,46(1):66-75.
    [79]邱德全,林永水,周近明.利玛原甲藻腹泻性毒素的生物学测定[J].热带海洋,1996,15(4):46-49.
    [80]中国海湾志编篡委员会.《中国海湾志》(第十一分册).北京:海洋出版社.1999:356-360.
    [81]周名江,颜天,邹景忠.长江口邻近海域赤潮发生区基本特征初探[J].应用生态学报.2003,14(7):1031-1038.
    [82]吴锋,江天久,张帆.浙江南麂海域双壳贝类的腹泻性贝毒分析[J].海洋环境科学,2010,29(4):492-495.
    [83]袁骐.舟山渔场及其邻近海域腹泻性贝类毒素的初步研究[J].水产学报,2002,26(6):528-532.
    [84]王颖.海南岛海岸环境特征[J].海洋地质动态,2002,18(3):1-9.
    [85]Vivini R. Eutrophication, marine biotoxin, humanhealth[J]. Science of the totalenvironment,1992:631-632.
    [86]Silvertw L, Cembella A D. Dynamic mode ling of phycotoxin kinetics in the bluemussel, Mytilus edulis,with implications for other marine invertebrates[J].FishAquat Sci,1995,52:521-531
    [87]曹际娟,唐守亭.试探应用贻贝进行海洋生物毒素跟踪监测的可行性[J].卫生研究,1998,27:103-106.
    [88]王俊,姜祖辉,唐启升.栉孔扇贝的滤食率与同化率.中国水产科学.2001,8(4):27-31.
    [89]Bayne B L. Relations between variable rates of growth, metabolic costs andgrowth efficiencies in individual Sydney rock oysters. J Exp Mar Bio Eco.2000,251:186-203.
    [90]GB17378.3-1998.《海洋监测规范》(第三部分)样品采集、贮存与运输[S].
    [91]张卫兵,许璞,周群霞.海产贝类食品安全预警研究.中国食品卫生杂志.2006,18(3):210-213.
    [92]Keith Davidson, Eileen Bresnan. Shellfish toxicity in UK waters: a threat tohuman health. Environmental Health,2009,8:11-15
    [93]华泽爱.赤潮灾害[M].北京:海洋出版社,1994,2-102

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