微囊藻和栅藻共培养实验及其竞争参数的计算

以Ｌｏｔｋａ－Ｖｏｌｔｅｒｒａ的双种竞争模型为基础,进行试验设计。共培养试验中,两种藻类的增长行为是不同的,培养前期共培养中栅藻的数量大于纯培养中栅藻的数量,而在后期则相反,微囊藻则是在整个共培养过程中的数量都小于纯培养中的数量。通过纯培养取得参数Ｋ和ｒ,变模型的微分形式为差分形式,以生长曲线拐点（密度制约起始点）出现的时间作为计算竞争参数的起始时间。经模拟计算获得参数,表明微囊藻的抑制能力是栅藻     

铜绿微囊藻和四尾栅藻在不同温度下的生长特性及竞争参数计算

在实验室条件下,对铜绿微囊（Microcystis aeruginosa）和四尾栅藻（Scendesmus quadricauda）分别在温度22℃、26℃和30℃下进行了纯培养和混合培养,实验结果显示温度对两种藻类的生长和竞争都有显著影响。微囊藻在22℃、26℃和30℃纯培养下的最大生物量及平均特定增长率（μ）分别为444、1180和998（×104cells/mL）及0.33、0.38和0.37/d,说明微囊藻在26℃和30℃下生长较好;混合培养下的最大生物量及平均特定增长率分别为270、778和647（×104cells/mL）及0.34、0.43和0.46/d,显示微囊藻在混合培养下受到了栅藻一定程度的竞争抑制。栅藻在22℃、26℃和30℃纯培养下的最大生物量及平均特定增长率分别为830、984和464（×104cells/mL）及0.36、0.34和0.32/d;混合培养下的最大生物及平均特定增长率分别为538、554和387（×104cells/mL）及0.43、0.40和0.39/d,说明栅藻在温度22℃、26℃下生长较好,混合培养下栅藻的生长受微囊藻影响较大。各温度下两种藻类的生长都可以用Logistic方程拟合。微囊藻对栅藻的抑制参数α分别为1.68（22℃）、0.65（26℃）和0.76（30℃）,而栅藻对微囊藻的抑制参数β依次为0.43（22℃）、0.51（26℃）和0.25（30℃）,三个温度下α均大于β,产生这一结果的原因可能是由于微囊藻与栅藻在竞争过程中不仅表现为资源竞争,同时还存在着明显的他感作用,且可推测微囊藻对栅藻的他感作用大于栅藻对微囊藻的,且在22℃时为最大。     

蓖齿眼子菜对栅藻和微囊藻的他感作用及其参数

主要报道篦齿眼子菜 (俗称红线草 )的种植水抽滤液对栅藻、微囊藻生长的他感作用试验。应用修正的逻辑斯谛 (Logistic)方程和Lotka Volterra种群竞争模型来计算篦齿眼子菜对藻类的他感作用参数。纯培养试验结果表明 :种植水抽滤液对栅藻生物量和生长率都有一定的促进作用。当浓度大于等于 5 0 %时 ,对栅藻生长的影响则是有抑制效应 ,他感作用效应与种植水的浓度没有明显的相关性 ,他感作用参数平均为 - 0 0 2 6。所有浓度设对照。微囊藻的生长都有明显的抑制作用 ,他感作用参数平均为 - 0 2 37。共培养试验结果表明 :篦齿眼子菜种植水抽滤液对纯培养试验结果有放大效应。所有的种植水抽滤液浓度对栅藻生长都起促进作用 ,对栅藻的生物量效应、生长率存在明显的对数正相关 ,但与他感作用参数的相关不明显 ,共培养的他感作用参数平均为 0 0 2 0 ;对微囊藻生长抑制作用更加明显 ,共培养的他感作用参数平均为 - 0 4 2 0。不管是纯培养还是共培养中 ,种植水抽滤液对栅藻的他感作用系数值都很低 ;而种植水抽滤液浓度对微囊藻的生物量效应、生长率或他感作用的参数都存在明显的线性负相关 ,并且他感作用系数值约高一个数量级     

铜绿微囊藻(Microcystis aeruginosa)对惠氏微囊藻(Microcystis wesenbergii)的化感作用

通过混合培养和添加过滤液两种方式观察铜绿微囊藻和惠氏微囊藻的生长曲线,探讨两种微囊藻之间的化感作用。结果表明:在混合培养条件下,两者能够形成相互抑制作用;当两者起始藻密度高于0.5×106cells.mL-1、混合比为1:1时,惠氏微囊藻的生长因化感作用而受到显著抑制(P<0.05),同时惠氏微囊藻也会对铜绿微囊藻产生一定的胁迫作用;处于对数生长期的铜绿微囊藻过滤液能抑制惠氏微囊藻的生长,且惠氏微囊藻起始藻密度低于0.5×106cells.mL-1,连续滴加该过滤液后,其生长受到极显著抑制(P<0.01)。     

铜绿微囊藻和四尾栅藻对铵态氮的响应

为探讨铵态氮在藻类种群演替中的作用,采用纯培养和共培养的方法,研究了铵态氮对铜绿微囊藻和四尾栅藻生长、生理和细胞形态的影响。结果表明:在纯培养条件下,5.0~20 mg·L~(-1)的铵态氮浓度适宜于铜绿微囊藻和四尾栅藻的生长,但铜绿微囊藻比四尾栅藻对铵态氮的响应更敏感;铵态氮浓度达到50 mg·L~(-1)时,铜绿微囊藻的光合活性在第2天时由0.35降低至0.07,四尾栅藻的光合活性则在第4天时由0.63降低至0.47;随着培养时间和铵态氮浓度的增加,四尾栅藻色素体的损伤情况加剧;铵态氮浓度≥10 mg·L~(-1)时,四尾栅藻易形成两细胞形态的结构,铵态氮浓度低于10 mg·L~(-1)时,四尾栅藻易形成四细胞形态的结构;在共培养条件下,适宜四尾栅藻和铜绿微囊藻生长的铵态氮浓度范围分别是0.5~2.0和5.0~20 mg·L~(-1);铜绿微囊藻是喜高铵(5.0~20 mg·L~(-1))的藻类,控制铵态氮浓度在一个较低水平(≤2.0 mg·L~(-1))可以作为防治微囊藻水华发生的策略。     

微囊藻毒素生态学研究

通过对微囊藻毒素的生态学进行综述,认为藻毒素的产生和含量的变化受水环境生物多样性、环境因子和微囊藻自身生物量等的影响。保障蓝藻在种群竞争、生态演替中获得竞争优势的各因素中,藻毒素发挥了重要调节作用。研究蓝藻的产毒机制,对于理解水体富营养化机制,实施蓝藻水华的生物控制,最终对富营养化水体进行生态修复具有重要的理论意义和现实作用;     

温度和氮磷浓度对平裂藻和栅藻生长及竞争的影响

为了解温度及氮磷浓度对平裂藻和栅藻生长及竞争的影响,分别在18、25和35℃条件下,以BG11培养基为基础,设置了不同的氮磷浓度组,进行了2种藻的单独培养试验和混合培养试验,结果表明:在纯培养条件下,低营养浓度组(磷浓度分别为0.1和0.5 mg/L)平裂藻在3种温度下基本停止生长,高营养盐浓度组(磷浓度分别为1.0和1.5 mg/L)除18℃1.0 mg/L组停止生长外,其余均能正常生长增殖,且细胞最大密度表现为25℃ 18℃ 35℃, 1.5和1.0 mg/L浓度组细胞生长差异不显著。栅藻在纯培养条件下,细胞密度总体表现为随着营养盐浓度升高而增加的趋势,细胞最大密度表现为18℃ 25℃ 35℃。在混合培养试验中,除35℃、1.5 mg/L组平裂藻对栅藻的竞争抑制参数大于栅藻对平裂藻的竞争抑制参数外,其余试验组均表现为栅藻受平裂藻影响较小。在混合培养体系中, 0.1 mg/L组平裂藻仍基本停止生长, 0.5 mg/L组受栅藻的刺激作用,生长优于纯培养体系。1.0和1.5 mg/L组均受栅藻的抑制作用,且浓度越高抑制作用越强。       

萼花臂尾轮虫培养滤液对铜绿微囊藻、斜生栅藻和小球藻群体形成及生长的影响

为探索浮游动物和藻类之间可能存在的信息传递,研究了萼花臂尾轮虫培养滤液对铜绿微囊藻、斜生栅藻和小球藻的生长及群体形成的影响.把萼花臂尾轮虫按1000个·L^-1的初始密度置于小球藻中培养24h后,用孔径0.15μm的微孔滤膜抽滤,得到轮虫培养滤液,此滤液中含有轮虫在生活过程中释放的一些信息化学物质.将轮虫培养滤液以20%的比例分别加入纯培养的铜绿微囊藻、斜生栅藻和小球藻中,进行为期7d的试验.结果表明,萼花臂尾轮虫培养滤液能显著地促进斜生栅藻的群体形成,而对铜绿微囊藻和小球藻在群体形成方面没有显著作用.另外,该滤液能显著提高小球藻种群的增长,对铜绿微囊藻和斜生栅藻的生长无明显影响.3种藻类对萼花臂尾轮虫的潜在牧食采取了不同的生态策略:斜生栅藻形成群体,增大摄食阻力,从而降低被摄食的风险;小球藻通过提高增长率来抵消被取食的损失;铜绿微囊藻是通过其它方式来降低被牧食(例如毒素).这些方式分别是这些藻类维持种群规模的反牧食防御策略之一.     

重金属铅与两种淡水藻的相互作用

为了研究重金属铅与淡水藻类之间的相互作用,采用不同Pb2+浓度处理铜绿微囊藻(Microcysis aeruginosa Kutz.)和斜生栅藻[Scenedesmus obliquus(Turp.)Kutz.],分别对两种藻的生物量、藻液电导率、O-·2含量、过氧化物酶(POD)、过氧化氢酶(CAT)活性以及藻对Pb2+的吸收作用等进行了测定,并通过扫描电镜观察了不同Pb2+浓度处理下两种藻细胞的表面结构。结果显示:(1)Pb2+浓度低于3 mg/L促进铜绿微囊藻生长,高于9 mg/L抑制其生长;但在3—12 mg/L范围内,Pb2+均明显抑制了斜生栅藻的生长,说明斜生栅藻对Pb2+毒性的敏感程度要高于铜绿微囊藻。(2)受到铅离子的胁迫,两种藻细胞膜通透性均有一定改变,扫描电子显微镜的照片观察,两种藻细胞表面的絮状物随着Pb2+的升高而增多,尤其是斜生栅藻细胞结构改变明显,多数细胞变形破裂;同时,O-·2含量升高,POD、CAT活性早期均可随Pb2+的增加而上升,表明氧自由基的产生增多以及由其引起的细胞生理生化改变可能是铅离子作用于藻细胞的主要机制。(3)两种淡水藻对Pb2+均有吸收作用,单位量藻细胞内,斜生栅藻对Pb2+的吸收能力好于铜绿微囊藻。所有结果提示:斜生栅藻不仅可以作为对重金属敏感的指示生物来监测水体Pb2+污染程度;同时由于斜生栅藻比铜绿微囊藻具有更好的Pb2+吸收能力,因此还可以利用斜生栅藻作为处理水体Pb2+的生物材料。     

超声波对铜绿微囊藻与蛋白核小球藻生理特征及竞争生长的影响

铜绿微囊藻是常见的水华蓝藻,常常在湖泊中与蛋白核小球藻共存或竞争生长。超声波可用于藻华即时治理,能够降低藻类生理活性,影响藻类生长,还可能改变藻类种间竞争关系。为了探究超声胁迫(35 kHz,0.035 W·cm^-3)对铜绿微囊藻与蛋白核小球藻的生理特征及种间竞争的影响,本研究设置纯藻组和1:1混合组(细胞浓度比)进行试验。结果表明: 铜绿微囊藻对超声胁迫更加敏感。超声处理600 s后,铜绿微囊藻的光合活性(F_v/F_m)和酯酶活性存在显著变化,纯藻组和混合组的F_v/F_m分别降低了51.8%和64.7%。而各组中蛋白核小球藻的光合活性变化较小。同时,铜绿微囊藻释放的荧光溶解性有机物(类色氨酸、类酪氨酸、类富里酸物质)含量多于蛋白核小球藻。两种藻的细胞浓度对超声波的响应也不同,蛋白核小球藻变化较小,而铜绿微囊藻的细胞浓度出现不同程度的下降。尤其是600 s超声处理大幅降低了混合组中铜绿微囊藻的细胞浓度(-42.6%),在超声胁迫解除后的8 d内蛋白核小球藻占优势,种间关系由铜绿微囊藻单边抑制蛋白核小球藻转变为两者互相抑制。在超声处理后,铜绿微囊藻的活性能够逐渐恢复,为了提高控藻效果的持久性,建议在一周后再次进行超声处理。     

Release of heptapeptide toxin (microcystin) during the decomposition process of Microcystis aeruginosa.

The decomposition process of toxic blue-green alga (cyanobacteria), Microcystis aeruginosa, under dark and aerobic condition was investigated in relation to the change of the amounts of heptapeptide toxins (microcystins YR and LR) by two experiments: one with Microcystis cells and the other with two purified microcystins. In the experiment with Microcystis cells, an increase of heterotrophic bacteria observed from the beginning of the experiment, was followed by decomposition of the algal cells and the subsequent release of microcystins into the filtrate fraction. The amounts of the toxins initially present in the cells were quantitatively detected in the filtrate fraction on the 35th day. The decomposition of microcystin YR began on the 42nd day. The decomposition rate of the two toxins was different. The decomposition rate of purified microcystins YR and LR, compared in distilled water and culture medium, respectively, indicated clearly that microcystin YR was more labile to decomposition than microcystin LR in the culture medium. At the end of the experiment (45th day) microcystin YR decreased to 58.6%, while 86.2% of microcystin LR remained.     

Competition for light between toxic and nontoxic strains of the harmful cyanobacterium Microcystis

The cyanobacterium Microcystis can produce microcystins, a family of toxins that are of major concern in water management. In several lakes, the average microcystin content per cell gradually declines from high levels at the onset of Microcystis blooms to low levels at the height of the bloom. Such seasonal dynamics might result from a succession of toxic to nontoxic strains. To investigate this hypothesis, we ran competition experiments with two toxic and two nontoxic Microcystis strains using light-limited chemostats. The population dynamics of these closely related strains were monitored by means of characteristic changes in light absorbance spectra and by PCR amplification of the rRNA internal transcribed spacer region in combination with denaturing gradient gel electrophoresis, which allowed identification and semiquantification of the competing strains. In all experiments, the toxic strains lost competition for light from nontoxic strains. As a consequence, the total microcystin concentrations in the competition experiments gradually declined. We did not find evidence for allelopathic interactions, as nontoxic strains became dominant even when toxic strains were given a major initial advantage. These findings show that, in our experiments, nontoxic strains of Microcystis were better competitors for light than toxic strains. The generality of this finding deserves further investigation with other Microcystis strains. The competitive replacement of toxic by nontoxic strains offers a plausible explanation for the gradual decrease in average toxicity per cell during the development of dense Microcystis blooms.     

D-Leu1]Microcystin-LR, from the cyanobacterium Microcystis RST 9501 and from a Microcystis bloom in the Patos Lagoon estuary, Brazil

[D-Leu1]Microcystin-LR was identified as the most abundant microcystin from a laboratory strain of the cyanobacterium Microcystis sp. isolated from a hepatotoxic Microcystis bloom from brackish waters in the Patos Lagoon estuary, southern Brazil. Toxicity of [D-Leu1]microcystin-LR, according to bioassay and protein phosphatase inhibition assay, was similar to that of the commonly-occurring microcystin-LR, which was not detectable in the Patos Lagoon laboratory isolate. This is the first report of a microcystin containing [D-Leu1] in the cyclic heptapeptide structure of these potent cyanobacterial toxins.     

利用PCR方法研究广州市景观湖产毒微囊藻的季节分布特点

为研究景观水体中产毒微囊藻的季节性分布特点,利用针对蓝藻和微囊藻的16srDNA、微囊藻毒素合成酶 mcyB 基因的部分核苷酸序列设计和筛选的特异性引物,对广州市内8个景观湖108份水样进行了冬季、夏季和秋季的二重及套式PCR的检测。结果显示,在冬季能被检测出的产毒微囊藻的阳性水样为42份,夏季为102份,而秋季为100份;阳性率分别为38.9%、94.4%、92.5%,产毒微囊藻在夏季和秋季阳性率高。结果表明在冬季、夏季和秋季均有产毒微囊藻分布;夏、秋季是广州市景观水体微囊藻污染的高峰季节,值得引起水文部门足够的重视。     

The ecological stoichiometry of toxins produced by harmful cyanobacteria: an experimental test of the carbon-nutrient balance hypothesis

The elemental composition of primary producers reflects the availability of light, carbon and nutrients in their environment. According to the carbon-nutrient balance hypothesis, this has implications for the production of secondary metabolites. To test this hypothesis, we investigated a family of toxins, known as microcystins, produced by harmful cyanobacteria. The strain Microcystis aeruginosa HUB 5-2-4, which produces several microcystin variants of different N:C stoichiometry, was cultured in chemostats supplied with various combinations of nitrate and CO₂. Excess supply of both nitrogen and carbon yielded high cellular N:C ratios accompanied by high cellular contents of total microcystin and the nitrogen-rich variant microcystin-RR. Comparable patterns were found in Microcystis -dominated lakes, where the relative microcystin-RR content increased with the seston N:C ratio. In total, our results are largely consistent with the carbon-nutrient balance hypothesis, and warn that a combination of rising CO₂ and nitrogen enrichment will affect the microcystin composition of harmful cyanobacteria.     

The abundance of microcystin-producing genotypes correlates positively with colony size in Microcystis sp. and determines its microcystin net production in Lake Wannsee

The working hypotheses tested on a natural population of Microcystis sp. in Lake Wannsee (Berlin, Germany) were that (i) the varying abundance of microcystin-producing genotypes versus non-microcystin-producing genotypes is a key factor for microcystin net production and (ii) the occurrence of a gene for microcystin net production is related to colony morphology, particularly colony size. To test these hypotheses, samples were fractionated by colony size with a sieving procedure during the summer of 2000. Each colony size class was analyzed for cell numbers, the proportion of microcystin-producing genotypes, and microcystin concentrations. The smallest size class of Microcystis colonies (<50 microm) showed the lowest proportion of microcystin-producing genotypes, the highest proportion of non-microcystin-producing cells, and the lowest microcystin cell quotas (sum of microcystins RR, YR, LR, and WR). In contrast, the larger size classes of Microcystis colonies (>100 microm) showed the highest proportion of microcystin-producing genotypes, the lowest proportion of non-microcystin-producing cells, and the highest microcystin cell quotas. The microcystin net production rate was nearly one to one positively related to the population growth rate for the larger colony size classes (>100 microm); however, no relationship could be found for the smaller size classes. It was concluded that the variations found in microcystin net production between colony size classes are chiefly due to differences in genotype composition and that the microcystin net production in the lake is mainly influenced by the abundance of the larger (>100- microm) microcystin-producing colonies.     

Effects of gibberellin A(3) on growth and microcystin production in Microcystis aeruginosa (cyanophyta)

Environmental factors that affect the growth and microcystin production of microcystis have received worldwide attention because of the hazards microcystin poses to environmental safety and public health. Nevertheless, the effects of organic anthropogenic pollution on microcystis are rarely discussed. Gibberellin A(3) (GA(3)) is a vegetable hormone widely used in agriculture and horticulture that can contaminate water as an anthropogenic pollutant. Because of its common occurrence, we studied the effects of GA(3) on growth and microcystin production of Microcystis aeruginosa (M. aeruginosa) PCC7806 with different concentrations (0.001-25mg/L) in batch culture. The control was obtained without gibberellin under the same culture conditions. Growth, estimated by dry weight and cell number, increased after the GA(3) treatment. GA(3) increased the amounts of chlorophyll a, phycocyanin and cellular-soluble protein in the cells of M. aeruginosa PCC7806, but decreased the accumulation of water-soluble carbohydrates. In addition, GA(3) was observed to affect nitrogen absorption of the test algae, but to have no effect on the absorption of phosphorus. The amount of microcystin measured by enzyme-linked immunosorbent assay (ELISA) increased in GA(3) treatment groups, but the stimulatory effects were different in different culture phases. It is suggested that GA(3) increases M. aeruginosa growth by stimulating its absorbance of nitrogen and increasing its ability to use carbohydrates, accordingly increasing cellular pigments and thus finally inducing accumulation of protein and microcystin.     

Towards clarification of the biological role of microcystins, a family of cyanobacterial toxins

Microcystins constitute a serious threat to the quality of drinking water worldwide. These protein phosphatase inhibitors are formed by various cyanobacterial species, including Microcystis sp. Microcystins are produced by a complex microcystin synthetase, composed of peptide synthetases and polyketide synthases, encoded by the mcyA-J gene cluster. Recent phylogenetic analysis suggested that the microcystin synthetase predated the metazoan lineage, thus dismissing the possibility that microcystins emerged as a means of defence against grazing, and their original biological role is not clear. We show that lysis of Microcystis cells, either mechanically or because of various stress conditions, induced massive accumulation of McyB and enhanced the production of microcystins in the remaining Microcystis cells. A rise in McyB content was also observed following exposure to microcystin or the protease inhibitors micropeptin and microginin, also produced by Microcystis. The extent of the stimulation by cell extract was strongly affected by the age of the treated Microcystis culture. Older cultures, or those recently diluted from stock cultures, hardly responded to the components in the cell extract. We propose that lysis of a fraction of the Microcystis population is sensed by the rest of the cells because of the release of non-ribosomal peptides. The remaining cells respond by raising their ability to produce microcystins thereby enhancing their fitness in their ecological niche, because of their toxicity.     

The Interactive Effects of Ammonia and Microcystin on Life-History Traits of the Cladoceran Daphnia magna: Synergistic or Antagonistic?

The occurrence of Microcystis blooms is a worldwide concern that has caused numerous adverse effects on water quality and lake ecology. Elevated ammonia and microcystin concentrations co-occur during the degradation of Microcystis blooms and are toxic to aquatic organisms; we studied the relative and combined effects of these on the life history of the model organism Daphnia magna. Ammonia and microcystin-LR treatments were: 0, 0.366, 0.581 mg L(-1) and 0, 10, 30, 100 μg L(-1), respectively. Experiments followed a fully factorial design. Incubations were 14 d and recorded the following life-history traits: number of moults, time to first batch of eggs, time to first clutch, size at first batch of eggs, size at first clutch, number of clutches per female, number of offspring per clutch, and total offspring per female. Both ammonia and microcystin were detrimental to most life-history traits. Interactive effects of the toxins occurred for five traits: the time to first batch of eggs appearing in the brood pouch, time to first clutch, size at first clutch, number of clutches, and total offspring per female. The interactive effects of ammonia and microcystin appeared to be synergistic on some parameters (e.g., time to first eggs) and antagonistic on others (e.g., total offspring per female). In conclusion, the released toxins during the degradation of Microcystis blooms would result, according to our data, in substantially negative effect on D. magna.     

Does microcystin disrupt the induced effect of Daphnia kairomone on colony formation in Scenedesmus?

In natural aquatic system, Scenedesmus and Microcystis species usually coexist. Microcystins are released into water after lysis of Microcystis cells during the collapse of heavy blooms. The released toxins can then come into contact with a wide range of aquatic organisms. In this study, we used filtered Daphnia test water containing kairomone from Daphnia magna to stimulate the inducible colony formation in Scenedesmus obliquus under microcystin-contaminated system, to examine how microcystin affects the induced effect of Daphnia kairomone on colony formation in S. obliquus. The results showed neither microcystin nor Daphnia kairomone affected the growth of S. obliquus. Microcystin neither promoted nor impaired the overall Daphnia-induced colony formation in S. obliquus, except reducing the proportion of eight-celled colonies on day 2, indicating that the effect of microcystin was just short-term and in general did not disrupt grazer-induced colony formation of S. obliquus.