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米氏凯伦藻生长对磷的响应及其吸收动力学研究
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  • 英文篇名:Studies on growth and phosphorous uptake kinetics of Karenia mikimotoi at the different phosphorous levels
  • 作者:周钦 ; 马增岭 ; 袁兴伟 ; 沈盎绿
  • 英文作者:ZHOU Qin;MA Zengling;YUAN Xingwei;SHEN Anglü;Zhejiang Provincial Key Laboratory for Subtropical Water Environment and Marine Biological Resources Protection,Wenzhou University;Key Laboratory of East China Sea & Oceanic Fishery Resources Exploitation and Utilization,Ministry of Agriculture,East China Sea Fisheries Research Institute;
  • 关键词:米氏凯伦藻 ; 无机磷 ; 生长 ; 吸收动力学
  • 英文关键词:Karenia mikimotoi;;inorganic phosphorus;;growth;;uptake kinetics
  • 中文刊名:SSDB
  • 英文刊名:Journal of Shanghai Ocean University
  • 机构:温州大学浙江省水环境与海洋生物资源保护重点实验室;中国水产科学研究院东海水产研究所农业部东海与远洋渔业资源开发利用重点实验室;
  • 出版日期:2017-07-15
  • 出版单位:上海海洋大学学报
  • 年:2017
  • 期:v.26
  • 基金:中央级公益性科研院所基本科研业务费专项资金项目(2015M06);; 国家自然科学基金青年项目(41506194);; 浙江省水环境与海洋生物资源保护重点实验室开放基金(KF201502);; 浙江省自然科学基金(LY14C030006);; 浙江省科技厅公益项目(2015C33246)
  • 语种:中文;
  • 页:SSDB201704008
  • 页数:8
  • CN:04
  • ISSN:31-2024/S
  • 分类号:68-75
摘要
研究了3种不同无机磷水平培养条件下对米氏凯伦藻(Karenia mikimotoi)细胞密度、体积的影响以及米氏凯伦藻的磷吸收动力学行为。结果表明:不同无机磷水平培养条件对米氏凯伦藻的生长有显著影响。在整个实验期间,磷浓度越高,米氏凯伦藻细胞密度越高,而且从第12天开始到实验结束,高磷组中米氏凯伦藻细胞密度均显著高于中磷组和低磷组(P<0.05);与之相反,低磷组中米氏凯伦藻细胞体积从第6天开始显著大于中磷和高磷组(P<0.05),而中磷组中米氏凯伦藻体积与高磷组差异不显著(P>0.05)。利用米氏方程可较好地拟合米氏凯伦藻对无机磷的吸收速率和初始磷浓度之间关系,其中米氏凯伦藻对无机磷的最大吸收速率(ρ_(max))为18.587 fmol/(cell·h),半饱和常数(K_s)为0.490μmol/L。鉴于东海赤潮高发区的海水中无机磷含量偏低的事实(0.10μmol/L左右),米氏凯伦藻对无机磷的较强亲和力以及低磷条件下的持续增长潜力表明在低磷条件下甲藻对营养盐的吸收比硅藻更具有竞争力,从而驱动东海区硅藻赤潮和甲藻赤潮演替。
        We conducted a series of conditional experiments to explore the changes in cell densities,volume and phosphorous uptake kinetics of Karenia mikimotoi at three different inorganic phosphorus levels.The results showed that the growth of K.mikimotoi was significantly affected by inorganic phosphorus levels,the cell densities in high-phosphorous(HP) group were significantly(P<0.05) higher than those in mediumphosphorous(MP) and low-phosphorous(LP) groups starting from the 12th day until to the end of experiment.On the contrary,the cell volume of K.mikimotoi which grew in LP group was significantly(P<0.05) greater than those in MP and HP groups from the 6th day,however,it was non-significantly different between MP and HP group(P>0.05).The relationship between inorganic phosphorus absorption rate and initial phosphorus concentration was preferably fitted by the Michaelis-Menten equation.According the equation,the maximum inorganic phosphorus absorption rate of K.mikimotoi(ρmax) was 18.587 fmol/(cell·h) and the half-saturation constant(Ks) was 0.490 μmol/L.Given the fact that inorganic phosphorus content was low(approximately 0.10 μmol/L) in the East China Sea when dinoflagellates red tides occurred,and K.mikimotoi have strong affinity for inorganic phosphorus and continuous growth potential in low phosphorus condition indicate that dinoflagellates have more competitive nutriment absorption ability than diatom,which may promote the succession of the diatom and dinoflagellates red tides in the East China Sea.
引文
[1]PAERL H W.Coastal eutrophication and harmful algal blooms:Importance of atmospheric deposition and groundwater as“new”nitrogen and other nutrient sources[J].Limnology and Oceanography,1997,42(5 part 2):1154-1165.
    [2]赵冬至.中国典型海域赤潮灾害发生规律[M].北京:海洋出版社,2010.ZHAO D Z.Occurrence regularity of marine red tide disaster in typical areas in China[M].Beijing:Marine Press,2010.
    [3]刘录三,李子成,周娟,等.长江口及其邻近海域赤潮时空分布研究[J].环境科学,2011,32(9):2497-2504.LIU L S,LI Z C,ZHOU J,et al.Temporal and spatial distribution of red tide in Yangtze River estuary and adjacent waters[J].Environmental Science,2011,32(9):2497-2504.
    [4]张勇,杨维东,李宏业,等.米氏凯伦藻对蒙古裸腹溞的毒性及致毒途径分析[J].生态毒理学报,2011,6(1):94-98.ZHANG Y,YANG W D,LI H Y,et al.Toxicity analysis of Karenia mikimotoi to Moina mongolica[J].Asian Journal of Ecotoxicolog,2011,6(1):94-98.
    [5]王朝晖,尹伊伟,齐雨藻,等.珠海桂山岛米氏裸甲藻赤潮对鱼鳃损伤的病理学组织观察[J].海洋学报,2001,23(1):133-138.WANG Z H,YI Y W,QI Y Z,et al.Histopathological changes in fish gills during Gymnodinium mikimotoi red tide in Guishan Island area,the South China Sea[J].Acta Oceanologica Sinica,2001,23(1):133-138.
    [6]YANG Z B,HODGKISS I J.Hong Kong's worst“red tide”—causative factors reflected in a phytoplankton study at Port Shelter station in 1998[J].Harmful Algae,2004,3(2):149-161.
    [7]SELLEM F,PESANDO D,BODENNEC G,et al.Toxic effects of Gymnodinium cf.mikimotoi unsaturated fatty acids to gametes and embryos of the sea urchin Paracentrotus Lividus[J].Water Research,2000,34(2):550-556.
    [8]MITCHELL S,RODGER H.Pathology of wild and cultured fish affected by a Karenia mikimotoi bloom in Ireland,2005[J].Bulletin of the European Association of Fish Pathologists,2007,27(1):39-42.
    [9]HANSEN G,DAUGBJERG N,HENRIKSEN P.Comparative study of Gymnodinium mikimotoi and Gymnodinium aureolum,Comb.Nov.(=Gyrodinium aureolum)based on morphology,pigment composition,and molecular data[J].Journal of Phycology,2000,36(2):394-410.
    [10]郑俊斌,张凤英,马凌波,等.米氏凯伦藻18S r DNA和转录间隔区序列分析[J].上海海洋大学学报,2009,18(6):680-685.ZHENG J B,ZHANG F Y,MA L B,et al.Sequence analysis of Karenia mikimotoi based on ribosomal 18S r DNA and internal transcribed space regions[J].Journal of Shanghai Ocean University,2009,18(6):680-685.
    [11]郑俊斌,张凤英,马凌波,等.两种常见外来入侵赤潮藻的PCR鉴定[J].海洋渔业,2009,31(3):325-329.ZHENG J B,ZHANG F Y,MA L B,et al.PCR identification of two alien invasive species of red tide algae[J].Marine Fisheries,2009,31(3):325-329.
    [12]张凤英,徐兆礼,马凌波,等.环介导恒温扩增技术快速检测米氏凯伦藻方法的建立[J].海洋学报,2009,31(6):170-175.ZHANG F Y,XU Z L,MA L B,et al.Loop-mediated isothermal amplification(LAMP)establishment for detection of Karenia mikimotoi(Dinophyceae)[J].Acta Oceanologica Sinica,2009,31(6):170-175.
    [13]边梅,郑森林,刘文华,等.应用实时荧光定量PCR技术研究九龙江口水域米氏凯伦藻的分布[J].台湾海峡,2012,31(1):65-71.BIAN M,ZHENG S L,LIU W H,et al.Application of realtime PCR for detection of Karenia mikimotoiin Jiulongjiang estuary waters[J].Journal of Oceanography in Taiwan Strait,2012,31(1):65-71.
    [14]STOECKER D,TILLMANN U,GRANELI E.Phagotrophy in harmful algae[M]//GRAN LI E,TURNER J T.Ecology of Harmful Algae.Berlin Heidelberg:Springer,2006,189:177-187.
    [15]BURKHOLDER J M,GLIBERT P M,SKELTON H M.Mixotrophy,a major mode of nutrition for harmful algal species in eutrophic waters[J].Harmful Algae,2008,8(1):77-93.
    [16]SMAYDA T J,REYNOLDS C S.Strategies of marine dinoflagellate survival and some rules of assembly[J].Journal of Sea Research,2003,49(2):95-106.
    [17]UCHIDA T,TODA S,MATSUYAMA Y,et al.Interactions between the red tide dinoflagellates Heterocapsa circularisquama and Gymnodinium mikimotoi in laboratory culture[J].Journal of Experimental Marine Biology and Ecology,1999,241(2):285-299.
    [18]周成旭,傅永静,严小军.4种典型有害赤潮原因种的溶血特性研究[J].生态毒理学报,2007,2(1):78-82.ZHOU C X,FU Y J,YAN X J.Hemolytic activity studies of several harmful alga strains[J].Asian Journal of Ecotoxicology,2007,2(1):78-82.
    [19]赵晓玮,唐学玺,王悠.两种海洋赤潮微藻赤潮异弯藻和米氏凯伦藻之间的相互作用[J].植物生态学报,2009,33(5):958-965.ZHAO X W,TANG X X,WANG Y.Interactions between two species of marine bloom microalgae under controlled laboratory conditions:Heterosigma akashiwo and Karenia mikimotoi[J].Chinese Journal of Plant Ecology,2009,33(5):958-965.
    [20]SHEN A L,YUAN X W,LIU G P,et al.Growth interactions between the bloom-forming dinoflagellates Prorocentrum donghaiense and Karenia mikimotoi under different temperature[J].Thalassas,2014,30(2):33-45.
    [21]SHEN A L,XING X L,LI D J.Allelopathic effects of Prorocentrum donghaiense and Karenia mikimotoi on each other under different temperature[J].Thalassas,2015,31(1):33-49.
    [22]崔伟民,杨维东,刘洁生,等.米氏凯伦藻溶血毒素的溶血反应特征[J].热带亚热带植物学报,2009,17(3):237-241.CUI W M,YANG W D,LIU J S,et al.Hemolytic properties of hemolytic extracts from Karenia mikimotoi Hasen[J].Journal of Tropical and Subtropical Botany,2009,17(3):237-241.
    [23]SATAKE M,SHOJI M,OSHIMA Y,et al.Gymnocin-A,a cytotoxic polyether from the notorious red tide dinoflagellate,Gymnodinium mikimotoi[J].Tetrahedron Letters,2002,43(33):5829-5832.
    [24]SATAKE M,TANAKA Y,ISHIKURA Y,et al.Gymnocin-B with the largest contiguous polyether rings from the red tide dinoflagellate,Karenia(Formerly Gymnodinium)mikimotoi[J].Tetrahedron Letters,2005,46(20):3537-3540.
    [25]曹春晖,刘文岭,施定基,等.不同氮磷浓度对米氏凯伦藻生长的影响[J].天津科技大学学报,2010,25(2):22-25.CAO C H,LIU W L,SHI D J,et al.Effects of nitrate and phosphate concentration on the growth of red tide species Karenia mikimotoi[J].Journal of Tianjing University of Science&Technology,2010,25(2):22-25.
    [26]沈盎绿,李道季.不同营养盐水平对东海原甲藻和米氏凯伦藻生长的影响[J].海洋渔业,2016,38(4):415-423.SHEN A L,LI D J.Effects of different nutrients levels on the growth of Prorocentrum donghaiense and Karenia mikimotoi[J].Marine Fisheries,2016,38(4):415-423.
    [27]赵晓玮.环境中不同氮磷营养盐浓度及氮源形态对米氏凯伦藻(Karenia mikimotoi)生长的影响研究[D].青岛:中国海洋大学,2010.ZHAO X W.Effects of the variously ambient nitrogen,phosphorus concentrations and nitrogen sources on growth of Karenia mikimotoi under laboratory conditions[D].Qingdao:Ocean University of China,2010.
    [28]SUN J,LIU D Y.Geometric models for calculating cell biovolume and surface area for phytoplankton[J].Journal of Plankton Research,2003,25(11):1331-1346.
    [29]中华人民共和国国家质量监督检验检疫总局,中国国家标准化管理委员会.GB 17378.4-2007海洋监测规范第4部分:海水分析[S].北京:中国标准出版社,2008.General Administration of Quality Supervision,Inspection and Quarantine of the People's Republic of China,Standardization Administration of the People's Republic of China.GB 17378.4-2007 The specification for marine monitoring—Part 4:Seawater analysis[S].Beijing:Standards Press of China,2008.
    [30]TOVAR-SANCHEZ A,SA UDO-WILHELMY S,GARCIAVARGAS M,et al.A trace metal clean reagent to remove surface-bound iron from marine phytoplankton[J].Marine Chemistry,2003,82(1/2):91-99.
    [31]HARRISON P J,PARSLOW J S,CONWAY H L.Determination of nutrient uptake kinetic parameters:a comparison of methods[J].Marine Ecology Progress Series,1989,52:301-312.
    [32]AKSNES D L,EGGE J K.A theoretical model for nutrient uptake in phytoplankton[J].Marine Ecology Progress Series,1991,70:65-72.
    [33]李雁宾.长江口及邻近海域季节性赤潮生消过程控制机理研究——浮游植物竞争生长三维生态动力学模型的建立与应用[D].青岛:中国海洋大学,2008.LI Y B.The Study of the seasonal occurrence mechanism of HABs in the Changjiang estuary and its Adjacent Sea[D].Qingdao:Ocean University of China,2008.
    [34]石岩峻,胡晗华,马润宇,等.塔玛亚历山大藻对氮和磷的吸收及其生长特性[J].应用生态学报,2003,14(7):1143-1146.SHI Y J,HU H H,MA R Y,et al.Nitrogen and phosphorus absorption and growth characteristics of Alexandrium tamarense[J].Chinese Journal of Applied Ecology,2003,14(7):1143-1146.
    [35]石岩峻,胡晗华,马润宇,等.不同氮磷水平下微小原甲藻对营养盐的吸收及光合特性[J].过程工程学报,2004,4(6):554-560.SHI Y J,HU H H,MA R Y,et al.Photosynthetic characteristics of Prorocentrum minimum and its nutrient uptake at different nitrogen and phosphorus levels[J].The Chinese Journal of Process Engineering,2004,4(6):554-560.
    [36]王金花,唐洪杰,杨茹君,等.氮磷营养盐对中肋骨条藻生长及硝酸还原酶活性的影响[J].海洋科学,2008,32(12):64-68.WANG J H,TANG H J,YANG R J,et al.The effects of nitrate and phosphate on the growth and nitrate reductase activity of Skeletonema costatum[J].Marine Sciences,2008,32(12):64-68.
    [37]FLYNN K J,FYNN K,JOHN E H,et al.Changes in toxins,intracellular and dissolved free amino acids of the toxic dinoflagellate Gymnodinium catenatum in response to changes in inorganic nutrients and salinity[J].Journal of Plankton Research,1996,18(11):2093-2111.
    [38]张璇,石晓勇,张传松,等.长江口及邻近海域赤潮藻种演替过程中营养盐特征[J].海洋环境科学,2012,31(6):817-820.ZHANG X,SHI X Y,ZHANG C S,et al.Nutrient characteristics in red-tide algal succession in Changjiang Estuary and adjacent sea areas[J].Marine Environmental Science,2012,31(6):817-820.
    [39]郭皓.中国近海赤潮生物图谱[M].北京:海洋出版社,2004.GU H.Illustrations of Planktons Responsible for the Blooms in Chinese Coastal Waters[M].Beijing:China Ocean Press,2004.
    [40]BUTTON D K.Biochemical basis for whole-cell uptake kinetics:specific affinity,oligotrophic capacity,and the meaning of the Michaelis constant[J].Apple and Environmental Microbiology,1991,57(7):2033-2038.
    [41]ZOU L,ZHANG J,PAN W X,et al.In situ nutrient enrichment experiment in the Bohai and Yellow Sea[J].Journal of Plankton Research,2001,23(10):1111-1119.
    [42]王丹,黄春秀,黄邦钦,等.黄海两种典型硅藻的磷胁迫生理研究[J].海洋科学,2008,32(5):22-27.WANG D,HUANG C X,HUANG B Q,et al.Physiological responses of two typical species of diatoms to phosphorus stress in Yellow Sea[J].Marine Sciences,2008,32(5):22-27.
    [43]张诚,邹景忠.尖刺拟菱形藻氮磷吸收动力学以及氮磷限制下的增殖特征[J].海洋与湖沼,1997,28(6):599-603.ZHANG C,ZOU J Z.Nutrient uptake kinetics and growth under nutrient limitation of Pseudonitzschia[J].Oceanologia et Limnologia Sinica,1997,28(6):599-603.
    [44]朱小明,沈国英,林均民.中华盒形藻对可溶性活性磷吸收动力学的研究[J].厦门大学学报(自然科学版),1993,32(2):230-235.ZHU X M,SHEN G Y,LIN J M.Studies on uptake kintics of soluble reactive phosphorus by Biddulphia sinensis Greviie[J].Journal of Xiamen University(Natural Science),1993,32(2):230-235.
    [45]李天深,于仁成,周名江.链状亚历山大藻(东海株)对磷营养物质的需求与吸收策略[J].海洋环境科学,2009,28(4):355-359.LI T S,YU R C,ZHOU M J.Demand and adsorption strategies of phosphorus of Alexandrium catenella isolated from East China Sea[J].Marine Environmental Science,2009,28(4):355-359.
    [46]李英,吕颂辉,徐宁,等.东海原甲藻对不同磷源的利用特征[J].生态科学,2005,24(4):314-317,321.LI Y,LS H,XU N,et al.The utilization of Prorocentrum donghaiense to four different types of phosphorus[J].Ecologic Science,2005,24(4):314-317,321.

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