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1.
聚球蓝细菌是Pico级浮游植物的重要组成部分,微型浮游动物对聚球蓝细菌的摄食是海洋微食物网研究的重要内容。实验室内测定微型浮游动物对聚球蓝细菌摄食速率的方法有饵料浓度差减法和体内饵料颗粒增多法2种,研究表明:鞭毛虫对聚球蓝细菌的摄食速率为0~2.9 syn grazer-1h-1,清滤速率0.4~10.9 nl grazer-1h-1;甲藻对聚球蓝细菌的摄食速率的范围为0.86~83.8 syn grazer-1h-1。实验室内研究纤毛虫对聚球蓝细菌摄食速率和清滤速率的资料不多。在自然海区,海水稀释培养、添加生物抑制剂培养和分粒级培养等方法被用来测定微型浮游动物对聚球蓝细菌摄食速率,海水稀释培养法表明微型浮游动物对聚球蓝细菌的摄食率大多低于0.9 d-1,最大为1.54 d-1;使用生物抑制剂方法获得的微型浮游动物对聚球蓝细菌的摄食率为0.04~1.06 d-1;海水分粒级培养法表明聚球蓝细菌的主要摄食者个体微小,绝大部分小于20μm。 相似文献
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生态学代谢理论(metabolic theory of ecology, MTE)指的是生物的代谢速度随着温度的升高而增加,随生物个体大小(即生物量)的增加而异速增长。根据MTE理论可预测异养过程与自养过程对温度的反应不同,低温对异养代谢的抑制要明显;而随着温度升高,异养代谢升高的速度比自养代谢升高的速度要快。MTE理论可以对海洋浮游微食物网生物的代谢研究进行理论指导,用于解释一些低温造成的海洋浮游生态学现象,以及预测全球变暖的影响。多年来人们一直根据MTE理论开展理论分析和实验检验,发现低温会抑制细菌和微型浮游动物的生长,并可以降低微型浮游动物的摄食率。春季高纬度海区的海水温度会抑制细菌的生长,而浮游植物则几乎不受影响,从而造成春季水华发生。温度和底物浓度是冷海(水温≤4℃)细菌生长率低的原因,但在永冷海(周年温度≤4℃的海区,包括极地海区和深海的大部分)中究竟是低温还是底物浓度限制了细菌的生长率仍被争论。全球变暖的预测认为本世纪海洋表层温度会升高2～6℃。根据MTE理论,温度升高对自养和异养过程的影响不同,围隔实验证明全球变暖将导致水华与细菌、水华与微型浮游动物的时滞变小,促进微型浮游动物对细菌和浮游植物的摄食,改变有机物质自养生产和异养消耗之间的平衡,使更多的物质和能量进入呼吸作用,使得生态系统变得更加异养。但在温度升高对海洋细菌生长效率和细菌生物量变化的研究方面,MTE理论还有一定的局限性,需要进一步的理论分析和实验检验。 相似文献
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冬季南海北部海域微型浮游动物及其对浮游植物摄食压力研究 总被引：1，自引：0，他引：1
2009年1月在南海北部海域的5个站位,采用稀释法和显微分析技术研究了浮游植物生长率及微型浮游动物对浮游植物的摄食压力,同时测定了微型浮游动物的丰度及类群组成.结果表明:南海北部微型浮游动物类群主要以无壳纤毛虫为主,南海北部微型浮游动物类群细胞丰度为33～529个/dm3.南海北部浮游植物生长率为0.45～1.83 d-1,微型浮游动物摄食率为0.44～1.76 d-1,摄食压力占浮游植物现存量的42.6%～82.8%,占初级生产力的97.3%～225.1%.近岸区摄食压力比陆架区高,表明冬季南海近岸区微型浮游动物摄食能够有效的控制浮游植物的生长,而陆架区浮游植物生长率大于摄食率,浮游植物存在着现存量的积累,微型浮游动物并不能完全控制浮游植物的生长. 相似文献
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2015年以广西三娘湾海域为亚热带海区,三亚海域为热带海区,利用稀释法开展了现场培养实验,测定热带和亚热带海区夜光藻对浮游植物、微型浮游动物对浮游植物的摄食压力,研究了夜光藻对不同粒径的浮游生物的摄食作用.结果表明:两个海区都有比较高的生长率和摄食率,其中细菌有最高的生长率和摄食死亡率;夜光藻的摄食率,从总浮游植物、微微型浮游植物到聚球藻、细菌逐渐增高.亚热带海区与热带海区相比,微型浮游动物的摄食压力更小,表明低温影响了浮游动物的摄食活性;而营养盐是引起亚热带海区高生长率的主要因素. 相似文献
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浮游桡足类是连接海洋初级生产者和较高营养级生物的关键类群,了解其食物组成是理解海洋生态系统中物质与能量流通途径的基础。本文通过分子生物学手段研究大亚湾三门岛海域桡足类优势种锥形宽水蚤(Temora turbinata)现场食物组成,共检测出6种食物类群(住囊虫、甲藻、绿藻、有孔虫类、棘皮类、苔藓类),住囊虫是主要被摄食的生物类群(45.94%),其次是青绿藻纲(Prasinophyceae)的微微型真核自养生物(29.73%),另外还检测出2种锥形宽水蚤可能摄食的赤潮甲藻种类(Takayama acrotrocha和Karlodinium veneficum)。研究结果揭示了在食物限制环境下锥形宽水蚤灵活的摄食策略,突出了浮游动物在摄食传递过程及生态系统中的关键地位,将有助于解释浮游动物摄食行为在维持近岸生态系统平衡与稳定性中的作用。 相似文献
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海洋浮游微食物网包括病毒、细菌、聚球藻蓝细菌、原绿球藻、微微型自养真核生物、微型浮游动物(混合营养和异养鞭毛虫、纤毛虫)等生物类群,其中病毒、细菌及微型浮游动物等异养生物类群是海洋中氮、磷营养盐再生的重要贡献者。海洋中细菌吸收还是释放营养盐取决于细菌与底物中元素的比例,在多数海区,异养细菌都是吸收营养盐。病毒主要通过溶解宿主来释放宿主细胞中的物质,释放的营养元素的存在形态大多为有机物。微型浮游动物对营养盐的再生主要通过排泄来完成,目前在实验室内测定微型浮游动物排泄率的研究比较少,进行研究的主要困难有两个:第一,微型浮游动物的室内培养较难;第二,测定微型浮游动物的代谢率技术难度较高。根据已有研究结果,鞭毛虫的单位体重排氮率为2.8~140μg N(mg DW)~(-1)h~(-1),最大排氮率为7.0×10-9~13.8×10-6μg NH4+N cell~(-1)h~(-1),再生效率为0~100%;最大排磷率为3.8×10-9~6.6×10-7μg P cell~(-1)h~(-1),再生效率为0~100%。鞭毛虫的营养盐排泄率和再生效率受鞭毛虫自身的生长阶段和生活策略、饵料中元素比例及温度的影响。纤毛虫的单位体重排氮率为0.25~178μg N(mg DW)~(-1)h~(-1),最大排氮率为1.59×10-7~1.2×10-4μg NH4+N cell~(-1)h~(-1);单位体重排磷率为13~363μg P(mg DW)~(-1)h~(-1),最大排磷率为0~1.3×10-5μg P cell~(-1)h~(-1)。影响纤毛虫排泄率和再生速率的主要因素为纤毛虫生长阶段和温度。自然海区测定微型浮游生物对营养盐的再生的方法主要为同位素稀释法,此外还可以根据其他资料推算微型浮游生物的营养盐再生速率及产生率以反映再生能力。多数野外实验结果证明微型浮游动物是营养盐主要的再生者。 相似文献
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海洋异养浮游细菌生物量及生产力的制约因素 总被引：15，自引：0，他引：15
根据海洋异养浮游细菌既是分解者，又是生产者的特点，从生态学方面探讨了海洋异养浮游细菌在海洋生态系统中的作用、研究现状及细菌生物量和生产力的制约因素。认为具有重要生态学意义的海洋异养浮游细菌生物量和生产力的主要影响因素有溶解性有机碳的性质及含量、无机营养盐浓度、海水温度、微量金属元素(如铁)含量、海洋异养浮游动物的摄食能力和噬菌体的感染等。 相似文献
8.
2005年7月在台湾海峡南部4个站位应用“稀释法”结合高效液相色谱(HPLC)色素分析技术研究了不同色素类群浮游植物的生长率及微型浮游动物对其的摄食死亡率.结果表明,不同色素类群浮游植物的生长率(k)和摄食死亡率(g)分别为0.52～ 1.34 d-1和0.25 ～ 1.10 d-1,微型浮游动物对不同色素类群浮游植物的现存量和初级生产力的摄食压力分别为22％～ 66％和40％～ 151％.通过比较不同类群浮游植物的g/k值,发现颗粒较大的浮游植物(硅藻和甲藻)的净生长率要大于那些微型藻类(蓝细菌、隐藻和定鞭金藻等)的净生长率,说明本次研究中微型藻类更易受到微型浮游动物的摄食控制. 相似文献
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《海洋科学集刊》2016,(0)
微食物环是海洋生态系统中重要的物质和能量过程,是传统食物链的有效补充。微食物环研究是当前海洋生态学研究的热点之一,但对其结构的系统研究较少,海洋微食物网结构在2000年才被Garrison提出。尽管微食物网各个类群的丰度在不同海洋环境中存在相对变化,但是这些变化都处于一定的范围之内,其丰度结构约为纤毛虫10cell/mL、鞭毛虫10~3cell/mL、微微型真核浮游生物10~4cell/mL、蓝细菌10~4~10~5cell/mL、异养细菌10~6cell/mL、病毒10~7particle/mL。海洋浮游食物链中捕食者和饵料生物粒径的最佳比值为10︰1,实际研究中该比值会略低,如纤毛虫与其饵料的粒径比值为8︰1,鞭毛虫为3︰1。微微型(pico-)和微型(nano-)浮游植物的丰度比(pico︰nano)是研究微食物网结构的指数之一,该指数具有不受研究尺度影响的优点,可用于研究区域性和全球性微食物网结构。近年来,学者们从多角度对海洋微食物网的结构开展了研究,针对不同海区微食物网各类群丰度、生物量时间和空间变化的研究有很多报道,微食物网的结构受空间、季节、摄食、营养盐等多种因素影响。在对不同空间微食物网的研究中,众多学者往往研究不同物理性质的水团中各类群生物丰度的不同,以此来表征微食物网结构的不同;同一海区微食物网结构的季节变化也是使用各个类群丰度和生物量的变化来表示,该变化主要受水文环境因素影响。摄食者对微食物网各类生物的影响通过3种途径:(1)中型浮游动物摄食;(2)中型浮游动物摄食微型浮游动物,通过营养级级联效应影响低营养级生物;(3)中型浮游动物通过释放溶解有机物、营养盐影响细菌和低营养级生物。浮游植物通过产生化感物质和溶解有机物影响微食物网结构,而营养盐的浓度及变化则可以对微食物网产生直接或间接影响。 相似文献
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微食物环是海洋生态系统中重要的物质和能量过程,是传统食物链的有效补充。微食物环研究是当前海洋生态学研究的热点之一,但对其结构的系统研究较少,海洋微食物网结构在2000年才被Garrison提出。尽管微食物网各个类群的丰度在不同海洋环境中有相对变化,但是这些变化都处于一定的范围之内,其丰度结构约为纤毛虫10 cell ml-1、鞭毛虫103 cell ml-1、微微型真核浮游生物104 cell ml-1、蓝细菌104-5 cell ml-1、异养细菌106 cell ml-1、病毒107 particle ml-1。海洋浮游食物链中捕食者和饵料生物粒径的最佳比值为10:1,实际研究中该比值会略低,例如纤毛虫与其饵料的粒径比值为8:1,鞭毛虫为3:1。Pico和Nano浮游植物的丰度比（Pico:Nano）是研究微食物网结构的指数之一,该指数具有不受研究尺度影响的优点,可用于研究区域性和全球性微食物网结构。近年来,学者们从多角度对海洋微食物网的结构开展了研究,不同海区微食物网各类群丰度、生物量的时间和空间变化研究有很多报道,微食物网的结构可受空间、季节、摄食、营养盐等多种因素影响。在对不同空间微食物网的研究中,学者往往研究不同物理性质的水团中各类群生物丰度的不同,以此来表征微食物网结构的不同;同一海区微食物网结构的季节变化也是使用各个类群丰度和生物量的变化来表示,该变化主要受水文环境因素影响。摄食者对微食物网各类生物的影响通过三种途径：1. 中型浮游动物摄食;2. 中型浮游动物摄食微型浮游动物,通过营养级级联效应影响低营养级生物;3. 中型浮游动物通过释放溶解有机物、营养盐影响细菌和低营养级生物。浮游植物通过产生化感物质和溶解有机物影响微食物网结构,而营养盐的浓度及变化则可以对微食物网产生直接或间接影响。 相似文献
11.
The source and significance of two nutrients, nitrogen and phosphorous, were investigated by a modified dilution method performed on seawater samples from the Jiaozhou Bay, in autumn 2004. This modified dilution method accounted for the phytoplankton growth rate, microzooplankton grazing mortality rate, the internal and external nutrient pools, as well as nutrient supplied through remineralization by microzooplankton. The results indicated that the phytoplankton net growth rate increased in turn from inside the bay, to outside the bay, to in the Xiaogang Harbor. The phytoplankton maximum growth rates and microzooplankton grazing mortality rates were 1.14 and 0.92 d-1 outside the bay, 0.42 and 0.32 d-1 inside the bay and 0.98 and 0.62 d-1 in the harbor respectively. Outside the bay, the remineralized nitrogen (Kr=24.49) had heavy influence on the growth of the phytoplankton. Inside the bay, the remineralized phosphorus(Kr=3.49) strongly affected the phytoplankton growth. In the harbor, the remineralized phosphorus (Kr=3.73) was in larger demand by phytoplankton growth. The results demonstrated that the different nutrients pools supplied for phytoplankton growth were greatly in accordance with the phytoplankton community structure, microzooplankton grazing mortality rates and environmental conditions. It is revealed that nutrient remineralization is much more important for the phytoplankton growth in the Jiaozhou Bay than previously believed. 相似文献
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稀释法(dilution technique)是研究微型浮游动物摄食和浮游植物生长的常用方法之一,负值浮游植物生长率是稀释实验中常见的现象。分析了造成负值生长率出现的因素,以及这些因素对实验结果的影响,并提出了防止不利影响产生的措施。负值生长率的出现不能简单地视为实验失败的标志,培养光照和温度条件、取样误差、无颗粒水污染、营养盐污染和限制等都可能造成负生长率的出现,且对实验结果的影响不同。同时,根据实验结果,演示浮游植物光适应、取样误差、无颗粒水污染和加富营养盐对稀释实验的影响。结果显示,光照条件可以改变细胞色素含量,且不同浮游植物类群对光照条件的响应不同,从而导致基于色素分析的稀释实验结果出现误差;取样混合不均,可造成取值偏低,导致浮游植物生长率估值偏低,甚至为负值,但可能不影响对摄食率的估算。另外,实验污染(无颗粒水和加富营养盐污染)往往会抑制浮游植物生长,甚至造成浮游植物死亡。因此,培养条件模拟和人为干扰控制是稀释实验成功的关键。 相似文献
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Phytoplankton growth and microzooplankton grazing were studied during the 2007 spring bloom in Central Yellow Sea. The surveyed stations were divided to pre-bloom phase (Chl a concentration less than 2 μg L−1), and bloom phase (Chl a concentration greater than 2 μg L−1). Shipboard dilution incubation experiments were carried out at 19 stations to determine the phytoplankton specific growth rates and the specific grazing rates of microzooplankton on phytoplankton. Diatoms dominated in the phytoplankton community in surface waters at most stations. For microzooplankton, Myrionecta rubra and tintinnids were dominant, and heterotrophic dinoflagellate was also important in the community. Phytoplankton-specific growth rates, with an average of 0.60±0.19 d−1, were higher at pre-bloom stations (average 0.62±0.17 d−1), and lower at the bloom stations (average 0.59±0.21 d−1), but the difference of growth rates between bloom and pre-bloom stations was not statistically significant (t test, p=0.77). The phytoplankton mortality rate by microzooplankton grazing averaged 0.41±0.23 d−1 at pre-bloom stations, and 0.58±0.31 d−1 during the blooms. In contrast to the growth rates, the statistic difference of grazing rates between bloom and pre-bloom stations was significant (after removal of outliers, t test, p=0.04), indicating the importance of the top-down control in the phytoplankton bloom processes. Average potential grazing efficiency on primary productivity was 66% at pre-bloom stations and 98% at bloom stations, respectively. Based on our results, the biomass maximum phase (bloom phase) was not the maximum growth rate phase. Both phytoplankton specific growth rate and net growth rate were higher in the pre-bloom phase than during the bloom phase. Microzooplankton grazing mortality rate was positively correlated with phytoplankton growth rate during both phases, but growth and grazing were highly coupled during the booming phase. There was no correlation between phytoplankton growth rate and cell size during the blooms, but they were positive correlated during the pre-bloom phase. Our results indicate that microzooplankton grazing is an important process controlling the growth of phytoplankton in spring bloom period in the Central Yellow Sea, particularly in the “blooming” phase. 相似文献
15.
Grazing impact of microzooplankton on phytoplankton in the Xiamen Bay using pigment-specific dilution technique 总被引：2，自引：0，他引：2
HUANG Bangqin LIU Yuan XIANG Weiguo TIAN Haojie LIU Hongbin CAO Zhenrui HONG Huasheng 《海洋学报(英文版)》2008,27(5):147-162
Phytoplankton group-specific growth and microzooplankton grazing were determined seasonally using the dilution technique with high-performance liquid chromatography （HPLC） in the Xiamen Bay, a subtropical bay in southeast China, between May 2003 and February 2004. The results showed that growth rates of phytoplankton ranged from 0.71 to 2.2 d^-1 with the highest value occurred in the inner bay in May. Mierozooplankton grazing rates ranged from 0.5 to 3.1 d^-1 with the highest value occurred in the inner bay in August. Microzooplankton grazing impact ranged from 39% to 95% on total phytoplankton Chl a biomass, and 65% to 181% on primary production. The growth and grazing rates of each phytoplankton group varied, the highest growth rate （up to 3.3 d^-1 ） was recorded for diatoms in August, while the maximum grazing rate （ up to 2.1 d ^-1 ） was recorded for chlorophytes in February in the inner bay. Among main phytoplankton groups, grazing pressure of microzooplankton ranged from 10% to 83% on Chl a biomass, and from 14% to 151% on primary production. The highest grazing pressure on biomass was observed for cryptophytes （83%） in August, while the maximum grazing pressure on primary production was observed for eyanobacteria （up to 151% ） in December in the inner bay. Net growth rates of larger phytoplanktons （diatoms and dinoflagellates） were higher than those of smaller groups （ prasinophytes, chlorophytes and cyanobacteria）. Relative preference index showed that microzooplankton grazed preferentially on prasinophytes and avoided to harvest diatoms in cold seasons （December and February）. 相似文献
16.
To elucidate iron regeneration and organic iron(III)-binding ligand formation during microzooplankton and copepod grazing on phytoplankton, incubation experiments were conducted in the western subarctic Pacific. During 8 days of dark incubation of ambient water and that amended with plankton concentrate, dissolved iron and organic iron(III)-binding ligands accumulated, approximately proportionally to the decrease in chlorophyll a. The observed increases in dissolved iron concentration were much greater than those expected from the consumption of phytoplankton biomass and previously reported Fe:C value of cultured algal cells, suggesting resolution from colloidal or particulate iron adsorbed onto the algal cell surface. When copepods were added to the ambient water, organic iron(III)-binding ligands accumulated more rapidly than in the control receiving no copepod addition, although consumed phytoplankton biomass was comparable between the two treatments. Bioassay experiment using filtrates collected from the incubation experiment showed that organic ligands formed during microzooplankton grazing reduced the iron bioavailability to phytoplankton and suppressed their growth. Moreover, picoplankton Synechococcus sp. and Micromonas pusilla were more suppressed by the organic ligands than the diatom Thalassiosira weissflogii. In conclusion, through microzooplankton and copepod grazing on phytoplankton, organic iron(III)-binding ligands as well as regenerated iron are released into the ambient seawater. Because the ligands lower iron bioavailability to phytoplankton through complexation and the degree of availability reduction varies among phytoplankton species, grazing by zooplankton can shift phytoplankton community structure in iron-limited waters. 相似文献
17.
Studies on growth rate and grazing mortality rate by microzooplankton of size-fractionated phytoplankton in spring and summer in the Jiaozhou Bay, China 总被引：15，自引：2，他引：13
1 Introduction Phytoplankton has been considered as a dom inantprim ary producer in m arine ecosystem s, starting them arine food chain (N ing and V aulot.,2003;Sun etal.,2001; Zhu et al., 2000; N ing and V aulot, 1992). A l-though potentialfates ofphytoplankton include advec-tion,verticalm ixing,sinking and m ortality due to virallysis and grazing (B anse,1994),m ortality due to graz-ing,especially by m icrozooplankton,is generally con- μm m esh to 25-L carboys, then transpo… 相似文献