Allelopathic effects of the Baltic cyanobacteria Nodularia spumdigena, Aphanizomenon flos-aquae and Anabaena lemmermannii on algal monocultures

Allelopathy, the release of extracellular compounds that inhibit the growth of other microorganisms, may be one factor contributing to the formation and/or maintenance of cyanobacterial blooms. We investigated the allelopathic effects of three cyanobacterial species (Nodularia spumigena, Aphanizomenon flos-aquae and Anabaena lemmermannii) that frequently form mass-occurrences in the Baltic Sea. We exposed monocultures of three phytoplankton species (Thalassiosira weissflogii, Rhodomonas sp. and Prymnesium parvum) to cell-free filtrates of the three cyanobacteria, and quantified allelopathic effects with cell counts. We also investigated the role of the growth phase of cyanobacteria in their allelopathy, by comparing the effects of an exponential and a stationary phase culture of N. spumigena. All tested cyanobacteria inhibited the growth of Rhodomonas sp., but none of them affected P. parvum. The effects on T. weissflogii were more variable, and they were amplified by repeated filtrate additions compared to a single filtrate addition. N. spumigena was more allelopathic in exponential than in stationary growth phase, whereas the culture filtrate was more hepatotoxic in stationary phase. Hepatotoxins were thus probably not involved in the allelopathic effects, which is also indicated by the allelopathic properties of the non-toxic A. flos-aquae and A. lemmermannii. The results demonstrate that the common Baltic cyanobacteria affect some coexisting phytoplankton species negatively. Allelopathy may therefore play a role in interspecific competition and contribute to cyanobacterial bloom maintenance.     

STIMULATING EFFECT OF ANABAENA SP. (CYANOBACTERIA) EXUDATE ON PRYMNESIUM PARVUM (HAPTOPHYTA)1

Prymnesium parvum blooms have become more frequent in the south‐central United States, leading to significant ecological and economic impacts. Allelopathic effects from cyanobacteria were suggested as a mechanism that might limit the development of P. parvum blooms. This research focused on the effects of cultured cyanobacteria, Anabaena sp., on P. parvum. Over a 6‐d period, daily additions of filtrate from the senescent Anabaena culture were made to P. parvum cultures growing in log phase. All treatments, including several types of controls, showed reductions in P. parvum biomass over the course of the experiment, but the treatments receiving Anabaena filtrate were reduced to a lesser degree, suggesting that filtrate from the senescent cyanobacteria culture was beneficial to P. parvum in some way. This unexpected outcome may have resulted from stimulation of heterotrophic bacteria by the addition of Anabaena filtrate, which likely contained exudates rich in dissolved organic carbon compounds. P. parvum was then able to supplement its nutritional requirements for growth by feeding on the elevated bacteria population. These findings coupled to previous observations suggest that interactions between cyanobacteria and P. parvum in natural environments are complex, where both allelopathic and growth‐stimulating interactions are possible.     

Allelopathic Effects of Toxic Haptophyte <Emphasis Type="Italic">Prymnesium parvum</Emphasis> Lead to Release of Dissolved Organic Carbon and Increase in Bacterial Biomass

The haptophyte Prymnesium parvum has lytic properties, and it affects coexisting phytoplankton species through allelopathy. We studied the effect of P. parvum allelochemicals on the lysis of the nontoxic and nonaxenic cryptomonad Rhodomonas salina and the consequent release of dissolved organic carbon (DOC). Changes in production, cell density, and biomass of associated bacteria were measured over 12 h. Six different combinations of P. parvum and R. salina cultures, their cell- and bacteria-free filtrates, and growth media as controls were used in the experiments. When P. parvum and R. salina cells were mixed, a significant increase in DOC concentration was measured within 30 min. Bacterial biomass increased significantly during the next 6 to 12 h when R. salina was mixed either with the P. parvum culture or the cell-free P. parvum filtrates (allelochemicals only). In contrast, bacterial biomass did not change in the treatments without the allelopathic action (without R. salina cells). Blooms of P. parvum alter the functioning of the planktonic food web by increasing carbon transfer through the microbial loop. In addition, P. parvum may indirectly benefit from the release of DOC as a result of its ability to ingest bacteria, by which it can acquire nutrients during limiting conditions.     

Competitive interactions between two allelopathic algal species: Heterosigma akashiwo and Phaeodactylum tricornutum

ABSTRACT

Both Heterosigma akashiwo and Phaeodactylum tricornutum have been reported to produce allelochemicals capable of inhibiting the growth of co-occurring microalgae. Here, potential allelopathy between H. akashiwo and P. tricornutum was evaluated using bi-algal culture, cell-free culture filtrate and a no-contact co-culturing system in nutrient-replete media. Experiments were also conducted in the no-contact co-culturing system under nutrient-limited conditions. In nutrient-replete bi-algal culture, the growth of P. tricornutum and H. akashiwo each tended to be strongly suppressed when the other species was inoculated at high cell densities. A mathematical model was used to simulate the growth interactions of the two species in bi-algal culture and showed that P. tricornutum outcompeted H. akashiwo over time with different initial cell densities under nutrient-sufficient conditions, indicating that P. tricornutum was more potent in allelopathy. Heterosigma akashiwo growth was inhibited both in the P. tricornutum culture filtrate and no-contact co-culturing system. This confirmed that the extracellular allelopathic compounds released by P. tricornutum were one of the sources of the H. akashiwo growth inhibition. Nutrient deficiency did not increase the extent of allelopathic activity of allelochemicals.     

The effects of aeration on growth and toxicity of Prymnesium parvum grown with and without algal prey

We investigated the effects of aeration on growth and toxicity of the haptophyte Prymnesium parvum in the presence and absence of the algal prey Rhodomonas salina. Batch monocultures of P-limited P. parvum and N and P sufficient R. salina and mixed cultures of the two microalgae were grown with no, low (20) and high (100) ml min⁻¹ aeration for 18 days. Cell growth of P. parvum and R. salina and cell toxicity of P. parvum were studied over the experimental period. The highest specific growth rates of P. parvum were found at low aeration rates. R. salina in monocultures showed typical growth patterns, while R. salina numbers declined rapidly in the mixed cultures. Of the initial cell densities, 98–100% of the R. salina cells were lysed or ingested within 24 h of mixing with P. parvum cells. The maxima P. parvum biomasses were significantly higher in the mixed cultures than in the monocultures. Cell toxicity of P. parvum increased significantly in response to aeration rates and the highest levels were found in the high aeration condition. Availability of prey and resupply of inorganic nutrients decreased P. parvum cell toxicity. Our study suggests that P. parvum is tolerant and is able to grow over a broad range of aeration and associated turbulence effects though low aeration represents an optimal condition for growth. As P. parvum toxicity was higher in the high aeration treatment we suggest that the higher concentrations of oxygen cause more toxins to be produced, as these are oxygen rich compounds. We suggest that oxygenation and turbulence of surface waters caused by mixing may be involved in promoting high toxic P. parvum blooms in shallow lakes and coastal waters.     

Removal of Prymnesium parvum (Haptophyceae) cells under different nutrient conditions by clay

In this study, we have shown that the ichthyotoxic Prymnesium parvum (haptophyte) can be successfully removed by spraying the surface with a phosphatic clay/polyaluminium chloride (PAC) mix (final concentration, 4 g l⁻¹ and 5 ppm, respectively). The alga was grown in non-axenic batch cultures with nitrogen deficient, phosphorus deficient and nutrient sufficient media. Sub-samples of the nutrient sufficient culture were diluted to obtain cell abundances equal to those in the nutrient deficient cultures. Clay/PAC removed up to 100% of the cells in the low cell nutrient sufficient treatment after 72 h, but removal in the other treatments was lower (up to 84%). The nitrogen deficient cells were found to be the most toxic, measured as haemolytic activity of the cells (HE₅₀), just prior to the start of the experiment. However, the toxicity of the cells in all treatments was found to fluctuate during the incubation time with a general increase in toxicity towards the end, suggesting that the cells became stressed during sedimentation and/or when trapped in the clay. But the amount of released toxins was always below the detection limit of the haemolytic assay, and the abundance of free-living bacteria, derived from flow cytometer counts, increased throughout the experiment. This suggests that released toxins were either trapped by the clay particles or effectively degraded by the bacterial community. The study shows that the clay method can be efficient in mitigation of P. parvum blooms, but further studies have to be conducted where optimum clay concentrations are determined to ensure that the efficiency is high against nutrient deficient cells and at high cell abundances, i.e. conditions found during blooms in eutrophic coastal waters, and to determine the fate of the cells and their toxins during and after sedimentation.     

Prymnesium parvum invasion success into coastal bays of the Gulf of Mexico: Galveston Bay case study

The toxic haptophyte Prymnesium parvum regularly forms fish-killing blooms in inland brackish water bodies in the south-central USA. Along the Texas coast smaller blooms have occurred in isolated areas. There appears to be an increasing risk that harmful P. parvum blooms will propagate into open coastal waters with implementation of future water plans. These plans will include increased interbasin water transfers from the Brazos River, regularly impacted by P. parvum blooms, to the San Jacinto-Brazos Coastal Basin, which ultimately flows into Galveston Bay (GB). Persisting source populations of P. parvum in inland waters elevates this risk. Thus, there is a need for an increased understanding of how P. parvum might perform in coastal waters, such as those found in GB. Here, two in-field experiments were conducted to investigate the influence of various plankton size-fractions of GB water on inoculated P. parvum during fall and winter, periods when blooms are typically initiating and developing inland. Stationary- and log-growth phase P. parvum were used to represent high and low toxicity initial conditions. Results revealed that P. parvum could grow in GB waters and cause acute mortality to silverside minnows (Menidia beryllina). Depending on season and growth phase, however, P. parvum growth and toxicity varied in different size fractions. During the fall, P. parvum inoculated from stationary-, but not log-growth phase culture, was negatively affected by bacteria-sized particles. During the winter, bacteria and nanoplankton together had a negative effect on P. parvum inoculated from stationary- and, to a lesser degree, log-growth phase cultures. Intermediate- and large-sized grazers when combined with bacteria and nanoplankton had complex relationships with inoculated P. parvum, sometimes stimulating and sometimes suppressing population growth. Toxicity to fish occurred in almost all plankton size fractions. The inclusion of progressively larger sized plankton fractions resulted in trends of decreased toxicity in treatments inoculated with stationary-, but not log-growth phase P. parvum in the fall. In the winter, however, inclusion of larger sized plankton fractions resulted in trends of increased toxicity to fish in treatments inoculated with both stationary- and log-growth phase P. parvum. This study indicates that understanding P. parvum population dynamics in open waters of estuaries and bays will be challenging, as there appears to be complex relationships with naturally occurring components of the plankton. The observations that P. parvum is able to grow to high population density and produce fish-killing levels of toxins underscores the need for advanced risk assessment studies, especially in light of water use plans that will result in P. parvum invasions of greater size.     

Removal of Prymnesium parvum (Haptophyceae) and its toxins using clay minerals

Laboratory experiments were conducted to examine the ability of several clay minerals from Sweden to remove the fish-killing microalga, Prymnesium parvum Carter, from suspension. In their commercial form (i.e. after incineration at 400 °C), seawater slurries (salinity = 26) of the three minerals tested were generally ineffective at removing P. parvum from culture within a range of 0.01 to 0.50 g/L, and after 2.5 h of flocculation and settling. Dry bentonite (SWE1) displayed the highest removal efficiency (RE) at 17.5%, with 0.50 g/L. Illite (SWE3) averaged only 7.5% RE between 0.10 to 0.50 g/L, while kaolinite (SWE2) kept the cells suspended instead of removing them. Brief mixing of the clay-cell suspension after SWE1 addition improved RE by a factor of 2.5 (i.e. 49% at 0.50 g/L), relative to no mixing. The addition of polyaluminum chloride (PAC, at 5 ppm) to 0.50 g/L SWE1 also improved RE to 50% relative to SWE1 alone, but only minor improvements in RE were seen with SWE2 and SWE2 combined with PAC. In further experiments, P. parvum grown in NP-replete conditions were removed in greater numbers than cells in N- or P-limited cultures, at 0.10–0.25 g/L of SWE1 and 5 ppm PAC. With 0.50 g/L, RE converged at 40% for all three culture conditions. The toxin concentration of NP-replete cultures decreased from 24.2 to 9.2 μg/mL (60% toxin RE) with 0.10–0.50 g/L SWE1 treatment and 5 ppm PAC. A strong correlation was found between cell and toxin RE (r²=0.995). For N-limited cultures, toxin RE ranged between 21 and 87% with the same clay/PAC concentrations, although the correlation between cell and toxin removal was more moderate (r²=0.746) than for NP-replete conditions. Interestingly, the toxin concentration within the clay-cell pellet increased dramatically after treatment, suggesting that clay addition may stimulate toxin production in N-stressed cells. For P-limited cultures, toxin concentration also decreased following clay/PAC treatment (i.e. 36% toxin RE), but toxin removal was poorly correlated to cell removal (r²=0.462). To determine whether incineration affected SWE1’s removal ability, a sample of its wet, unprocessed form was tested. The RE of wet bentonite (SWE4) was slightly better than that of SWE1 (31% versus 17%, respectively, at 0.50 g/L), but when 5 ppm PAC was added, RE increased from 10 to 64% with 0.05 g/L of SWE4, and increased further to 77% with 0.50 g/L. There were no significant differences in RE among NP-replete, N-limited and P-limited cultures using PAC-treated SWE4. Finally, RE varied with P. parvum concentration, reaching a maximum level at the lowest cell concentration (1×10³ cells/mL): 100% RE with 0.10 and 0.50 g/L SWE4 + 5 ppm PAC. RE dropped as cell concentration increased to 1×10⁴ and 5×10⁴ cells/mL, but rose again when concentration increased to 1×10⁵ cells/mL, the concentration used routinely for the removal experiments above. Based on these results, SWE4 with PAC was the most effective mineral sample against P. parvum. Overall, these studies demonstrated that clay flocculation can be effective at removing P. parvum and its toxins only under certain treatment conditions with respect to cell concentration, clay type and concentration, and physiological status.     

Changes in alkaline phosphatase activity and phosphate uptake in P-limited phytoplankton,induced by light intensity and spectral quality

Alkaline phosphatase activity and P uptake were determined in P-limited Dunaliella tertiolecta, Thalassiosira pseudonana, Phaeodactylum tricornumtum, and Prymnesium parvum grown under different light intensities and colors. Both intracellular and extracellular enzyme activities varied with the intensity and quality of light in a species-specific manner. The spectral composition of the light also affected P uptake kinetics. No correlation was found between enzyme activity and V_max both within a species and for pooled data for all four species, indicating that the change in uptake kinetics and enzyme activity was not related to P limitation, but induced by the light conditions. Changes in the optimum N:P ratio induced by light were also not related to P uptake kinetics or enzyme activity. These data suggest that light conditions may in themselves have profound effects on species competition for limiting nutrients. Furthermore, since both alkaline phosphatase activity and P uptake were influenced by the prevailing light conditions we suggest that these parameters be used cautiously when determining the P nutritional status of phytoplankton in nature.Address for reprint requests     

Identification of toxic fatty acid amides isolated from the harmful alga Prymnesium parvum carter

The golden alga Prymnesium parvum has been implicated in fish and aquatic animal kills globally for over a century. In addition to widespread ecological impacts through the loss of entire fish populations within lakes, an economic burden is also felt by state and local agencies due to year class losses of fish raised for stocking lakes as well as loss of fishing and recreational use of the affected water. Multiple compounds have been implicated in P. parvum toxicity, but the unequivocal identification and characterization of all P. parvum toxins remained to be accomplished. To unambiguously characterize these toxins, we analyzed laboratory-cultured cells exposed to limited nitrogen and phosphorus concentrations, uni-algal wild cells collected from an ichthytoxic bloom event at Lake Wichita, TX, and the water from both cultured and field-collected algae. A bioassay-guided fractionation process was employed to chemically isolate P. parvum toxins using both mammalian cells and larval fish. The results of these assays revealed that there was a distinct similarity in the toxic compounds characterized as seven primary fatty acid amides (myristamide, palmitamide, linoleamide, oleamide, elaidamide, stearamide, and erucamide) and one hydroxamic acid (linoleyl hydroxamic acid). These compounds display cytotoxic and ichthytoxic activity and have not yet been reported in P. parvum toxicity or in the toxicity of harmful algal species.     

Fish kills related toPrymnesium parvum N. Carter (Haptophyta) in the People's Republic of China

Prymnesium parvum has been known to cause mass mortality of fish in PR of China since 1963. It usually occurs in brackish waters and inland high-mineral waters. The fish-breeding industry (mainly species of carp) in these regions of the PRC has been threatened by this microalga. Electron microscopic examination of isolates from Dalian and Tianjin revealed that the isolates wereP. parvum, based on specific scale patterns and two kinds of scales. The symptoms of the poisoned fish and the control of this toxic alga are also discussed. The addition of ammonium sulfate, copper sulfate, mud, reduced salinity and organic fertilizer to fish ponds has been partially successful in controlling blooms of this toxic alga. Adding 50–70 kg ha^–1 day^–1 manure (dry weight) to the fish pond to inhibitP. parvum from becoming the dominant species in the fish pond is recommended. A reduction in salinity to less than 2 is the easiest way to save freshwater fish from being poisoned byP. parvum. Use of ammonium sulfate is an efficient, economical and safer method to controlP. parvum than copper sulfate or mud.     

Ethionine and Methionine Metabolism by the Chrysomonad Flagellate Prymnesium parvum

SYNOPSIS. Ethionine or methionine can serve as sole nitrogen source for growth of Prymnesium parvum. Both amino acids are taken up as such at a ratio of 2 : 1 methionine/ethionine. Ethionine is totally de-ethylated in the cell, while methionine is probably only partially de-methylated. The homocysteine moiety of both amino acids is similarly metabolised to form cysteine or re-methylated to form methionine. De-ethylation of ethionine seems how P. parvum avoids its antimetabolic effect     

The hidden flora of a lake

Summary Twenty-seven water samples taken from the Sea of Galilee, Israel, were enriched selectively with an inorganic salt medium to further the appearance of halophilic algae, rare or unknown from the lake. The Chrysophycean flagellatePrymnesium parvum, known to cause toxic blooms, has been especially looked for.A radical change in the algal composition of the enriched samples could be observed. Out of 31 species that proliferated in the so established cultures, 11 were new to the lake. Fifteen species belonged to the Cyanophyceae, 8 to the Diatomeae, and 7 species belonged to the Chlorophyceae. Prymnesium parvum could be found in 6 out of the 27 samples.It is concluded that in case of a sufficient rise in the lake's salinity, halophilic algae that are now rare or dormant in the lake, will replace the present algal flora. The presence in the lake ofPrymnesium parvum forms a potential danger of toxic blooms.

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Résumé Vingt-sept échantillons d'eau prélevés dans le Lac de Tibériade, Israel, ont été enrichis sélectivement par des milieux salins inorganiques afin de stimuler le développement d'algues halophiles rares ou inconnues dans le lac. Notre attention a été particulièrement attirée par la présence du Chrysophyte flagélléPrymnesium parvum, qui provoque des pullulations toxiques dans L'eau.Nous avons pu observer un changement radical dans la composition floristique des échantillons enrichis. Parmi les 31 espèces qui se sont développées dans nos cultures, 11 espèces sont inconnues dans le lac; 15 espèces appartiennent aux Cyanophyceae, 8 aux Diatomées et 7 aux Chlorophyceae. Nous avons trouvéPrymnesium parvum dans 6 échantillons sur 27.Nous pouvons conclure, qu'en cas d'accroissement du taux de la salinité dans le lac, les algues halophiles, actuellement rares ou dormantes, remplaceront la flore présente.Les possibles pullulations toxiques dePrymnesium parvum dans les eaux du Lac constituent donc un danger permanent.

     

Feeding by ciliates on two harmful algal bloom species, Prymnesium parvum and Prorocentrum minimum

We have focused on ciliates as potential grazers on toxic phytoplankton because they are major herbivores in aquatic food webs. Ciliates may exert top down control on toxic phytoplankton blooms, potentially suppressing or shortening the duration of harmful algal blooms (HABs). We measured the growth rates of several ciliate species on uni-algal and mixed diets of both HAB and non-HAB algae. The tintinnids Favella ehrenbergii, Eutintinnus pectinis and Metacylis angulata and the non-loricate ciliates Strombidinopsis sp. and Strombidium conicum were isolated from Long Island Sound (LIS), and fed HAB species including the prymnesiophyte Prymnesium parvum (strain 97-20-01) and the dinoflagellate Prorocentrum minimum (strains Exuv and JA 98-01). Ciliates were fed algal prey from cultures at various growth phases and at varying concentrations. We observed no harmful effects of P. minimum (Exuv) on any of the ciliates. However in a comparison of strains, P. minimum (Exuv) supported high growth rates, whereas P. minimum (JA 98-01) supported only nominal growth. P. parvum was acutely toxic to ciliates at high concentrations (2×10⁴–3×10⁴ cells ml⁻¹). At low concentrations (5×10³–1×10⁴ cells ml⁻¹), or in culture filtrate, ciliates survived for at least several hours. In mixed diet experiments, as long as a non-toxic alga was available, ciliates survived and at times grew well at concentrations of P. parvum (5×10²–3×10⁴ cells ml⁻¹) that would otherwise have killed them. The present study suggests that prior to the onset of toxicity and bloom formation ciliates may exert grazing pressure on these HAB species, potentially contributing to the suppression or decline of P. minimum and P. parvum blooms.     

强壮前沟藻化感物质分析

微藻化感作用是一种极其复杂的生理、生态学现象。选取强壮前沟藻指数生长初期Ⅰ和平台生长初期Ⅱ两个阶段的滤液对中肋骨条藻、海洋原甲藻、锥状斯氏藻及球等鞭金藻生长的影响进行了研究,并萃取了阶段Ⅱ的粗提物,抑藻检测表明其具有"杀藻"效应,通过GC/MS分析该粗提物中具有潜在化感作用的物质种类。研究发现强壮前沟藻两个生长阶段的滤液对中肋骨条藻均产生强烈致死效应(phaseⅠ:F=15.18475,P=0.00298<0.05;phaseⅡ:F=6.24559,P=0.03149<0.05);锥状斯氏藻在强壮前沟藻滤液中生长,实验结束时两个阶段中的细胞密度分别是对照组的79.3%和68.9%;海洋原甲藻在强壮前沟藻生长阶段Ⅱ滤液实验的最后3d,其生长受到显著抑制(F=4.84438,P=0.04925<0.05);而等鞭金藻在强壮前沟藻两个生长阶段滤液中被抑制现象不明显(P>0.05)。强壮前沟藻滤液实验表明,强壮前沟藻能够向微环境中分泌代谢产物来抑制中肋骨条藻和海洋原甲藻的生长,并且这种抑制效应具有种类特殊对应性。上述实验结果还表明,强壮前沟藻生长阶段Ⅱ的滤液具有的生长抑制作用较为明显。采用乙酸乙酯萃取强壮前沟藻生长阶段Ⅱ滤液中的代谢产物,检测发现其代谢粗提物具有溶藻效应,GC/MS分析结果表明粗提物中存在4种可能产生化感抑制作用的物质,其中二丁基羟基甲苯(Butylated Hydroxytoluene BHT)被认为具有抗滤过性病原体和抗微生物活性。     

Allelopathic potential of an annual weed,Polypogon monspeliensis,in crops in India

The question of whether annual weeds are allelopathic under natural conditions still remains to be critically answered. Investigations were carried out to understand the involvement and mode of operation of allelopathy in an annual weed, Polypogon monspeliensis. Comparative studies of soils associated with and without the weed under field conditions revealed that there was no significant difference in toxicity of the two soils, and thus the possibility of its allelopathic effect on crops grown in the same season could be ruled out. However, soil amended with weed straw had significantly higher total phenolics including higher relative concentrations of phenolic fractions that were not detected in unamended soil. Phenolic fractions significantly affected the seedling growth of radish and cluster bean. It is likely that P. monspeliensis did not interfere chemically with the crops cultivated during the same season, but interfered with the following season crop through incorporated straw. These results indicate how a monocarpic annual such as P. monspeliensis can be allelopathic under field conditions and allelopathic potential can be managed. We suggest that before detailed investigations on allelopathy are performed as per earlier recommended protocols, data on weed life cycle pattern and agricultural practices should be collected.     

Behavioural differences underlie toxicity and predation variation in blooms of Prymnesium parvum

Much of the evolutionary ecology of toxic algal blooms (TABs) remains unclear, including the role of algal toxins in the adaptive ‘strategies’ of TAB-forming species. Most eukaryotic TABs are caused by mixotrophs that augment autotrophy with organic nutrient sources, including competing algae (intraguild predation). We leverage the standing diversity of TABs formed by the toxic, invasive mixotroph Prymnesium parvum to identify cell-level behaviours involved in toxin-assisted predation using direct observations as well as comparisons between genetically distinct low- and high-toxicity isolates. Our results suggest that P. parvum toxins are primarily delivered at close range and promote subsequent prey capture/consumption. Surprisingly, we find opposite chemotactic preferences for organic (prey-derived) and inorganic nutrients between differentially toxic isolates, respectively, suggesting behavioural integration of toxicity and phagotrophy. Variation in toxicity may, therefore, reflect broader phenotypic integration of key traits that ultimately contribute to the remarkable flexibility, diversity, and success of invasive populations.     

Allelopathic effects of the submerged macrophyte <Emphasis Type="Italic">Potamogeton malaianus</Emphasis> on <Emphasis Type="Italic">Scenedesmus obliquus</Emphasis>

Allelopathic effects of the submerged macrophyte Potamogeton malaianus on Scenedesmus obliquus were assessed using a two-phase approach under controlled laboratory conditions. In the co-culture experiment (phase І), the growth of S. obliquus at two different initial cell densities was significantly inhibited by P. malaianus. Moreover, the growth inhibition was dependent on the biomass density of P. malaianus. Antioxidant enzymes (SOD, CAT and POD), MDA, APA, total soluble protein, protein electrophoretic pattern and morphology of S. obliquus were determined after the co-culture experiment was terminated. The activities of SOD, CAT, POD and APA at the low initial cell density were stimulated, the contents of MDA and total soluble protein were increased, and some special protein bands disappeared in P. malaianus treatments. The macrophyte had no effect on the activities of SOD and APA at the high initial cell density, but significantly influenced other physiological parameters of S. obliquus with the increase of biomass density. The morphology of S. obliquus showed no difference in the macrophyte treatments and the controls, and the cultures were dominated by 4-celled coenobia. The results indicated P. malaianus had significant allelopathic effects on the growth and physiological processes of S. obliquus. Moreover, the allelopathic effects depended on initial algal cell density, biomass density of the macrophyte, and their interaction. In the experiment of P. malaianus culture filtrates (phase II), filtrates from combined culture of plant and S. obliquus at the low initial cell density exhibited no apparent growth inhibitory effect on S. obliquus. The result showed that initial addition of growth-inhibiting plant filtrates had no allelopathic effect on S. obliquus. We concluded that the allelopathic effects on S. obliquus were found in the presence of P. malaianus, but not in P. malaianus filtrates. However, the absence of allelopathic effect on S. obliquus might be due to the very low concentrations of allelochemicals in the filtrates. Handling editor: S. M. Thomas