Abstract:The phytoplankton in warm oligotrophic regions of the open oceans is dominated by Ͻ2-m cells too small for efficient direct consumption by mesozooplankton. However, these primary producers are hypothetically linked to higher trophic levels via the cascading impacts of mesozooplankton grazing on intermediate consumers. To assess the magnitudes of these indirect trophic linkages, grazing experiments, involving different concentration treatments of the mixed mesozooplankton community, were performed during cruise… Show more
“…The overall net effect of mesozooplankton feeding on phytoplankton in marine environment is counter-balanced by two opposite effects: direct consumption and indirect cascading (nutrient recycling is not considered here; Calbet and Landry, 1999). The trophic interactions are particularly complex in subtropical coastal and estuarine environments where planktonic abundances, compositions and mesozooplankton feeding preferences are temporally variable because of dynamic hydrographic conditions (Gifford et al, 2007 and this study).…”
Section: Discussion the Net Effect Of Mesozooplankton Feeding On Phytmentioning
confidence: 99%
“…Generally, small-sized phytoplankton (<5 µm) were the preferential food items for microzooplankton, while they were generally too small to be directly ingested by the majority of mesozooplankton species (Calbet and Landry, 1999;Froneman, 2002;Liu and Dagg, 2003;Liu et al, 2005a and this study). A parallel study of our research through HPLC pigment analysis also showed that the clearance rates of mesozooplankton on small-sized phytoplankton, green algae and Synechococcus, were generally negative due to trophic cascades (Liu et al, 2010).…”
Section: The Effect Of Mesozooplankton Size-selective Feedingmentioning
In order to understand how mesozooplankton assemblages influenced phytoplankton in coastal and estuarine waters, we carried out a monthly investigation on mesozooplankton composition at two contrasting stations of Hong Kong coastal and estuarine waters and simultaneously conducted bottle incubation feeding experiments. The assemblage of mesozooplankton was omnivorous at both stations with varying carnivory degree (the degree of feeding preference of protozoa and animal food to phytoplankton) and the variations of carnivory degree were significantly associated with microzooplankton biomass (ciliates for the coastal station, both ciliates and dinoflagellates for the estuarine stations) and physical environmental parameters (primarily salinity). High carnivory was primarily due to high composition of noctilucales, Corycaeus spp., Oithona spp. and Acartia spp. Results of feeding experiments showed that grazing impacts on phytoplankton ranged from −5.9 to 17.7%, while the mean impacts were just <4% at both stations. The impacts were size-dependent, by which mesozooplankton consumed around 9% of large-sized phytoplankton while indirectly caused an increase of 4% of small-sized phytoplankton. Mesozooplankton clearance rate on phytoplankton, calculated from the log response of chlorophyll a concentrations by the introduction of bulk grazers after 1-day incubation, was significantly reduced by increasing carnivory degree of the mesozooplankton assemblage. The mechanism for the reduction of mesozooplankton clearance rate with increasing carnivory degree was primarily due to less efficient of filtering feeding and stronger trophic cascades due to suppression of microzooplankton. The feeding rates of mesozooplankton on microzooplankton were not obtained in this study, but the trophic cascades indirectly induced by mesozooplankton carnivorous feeding can be observed by the negative clearance rate on small-sized phytoplankton. Overall, the main significance of this study is the empirical relationship between carnivory degree and clearance rate, which allow researchers to potentially predict the herbivory of mesozooplankton in the nature without conducting feeding experiments.
“…The overall net effect of mesozooplankton feeding on phytoplankton in marine environment is counter-balanced by two opposite effects: direct consumption and indirect cascading (nutrient recycling is not considered here; Calbet and Landry, 1999). The trophic interactions are particularly complex in subtropical coastal and estuarine environments where planktonic abundances, compositions and mesozooplankton feeding preferences are temporally variable because of dynamic hydrographic conditions (Gifford et al, 2007 and this study).…”
Section: Discussion the Net Effect Of Mesozooplankton Feeding On Phytmentioning
confidence: 99%
“…Generally, small-sized phytoplankton (<5 µm) were the preferential food items for microzooplankton, while they were generally too small to be directly ingested by the majority of mesozooplankton species (Calbet and Landry, 1999;Froneman, 2002;Liu and Dagg, 2003;Liu et al, 2005a and this study). A parallel study of our research through HPLC pigment analysis also showed that the clearance rates of mesozooplankton on small-sized phytoplankton, green algae and Synechococcus, were generally negative due to trophic cascades (Liu et al, 2010).…”
Section: The Effect Of Mesozooplankton Size-selective Feedingmentioning
In order to understand how mesozooplankton assemblages influenced phytoplankton in coastal and estuarine waters, we carried out a monthly investigation on mesozooplankton composition at two contrasting stations of Hong Kong coastal and estuarine waters and simultaneously conducted bottle incubation feeding experiments. The assemblage of mesozooplankton was omnivorous at both stations with varying carnivory degree (the degree of feeding preference of protozoa and animal food to phytoplankton) and the variations of carnivory degree were significantly associated with microzooplankton biomass (ciliates for the coastal station, both ciliates and dinoflagellates for the estuarine stations) and physical environmental parameters (primarily salinity). High carnivory was primarily due to high composition of noctilucales, Corycaeus spp., Oithona spp. and Acartia spp. Results of feeding experiments showed that grazing impacts on phytoplankton ranged from −5.9 to 17.7%, while the mean impacts were just <4% at both stations. The impacts were size-dependent, by which mesozooplankton consumed around 9% of large-sized phytoplankton while indirectly caused an increase of 4% of small-sized phytoplankton. Mesozooplankton clearance rate on phytoplankton, calculated from the log response of chlorophyll a concentrations by the introduction of bulk grazers after 1-day incubation, was significantly reduced by increasing carnivory degree of the mesozooplankton assemblage. The mechanism for the reduction of mesozooplankton clearance rate with increasing carnivory degree was primarily due to less efficient of filtering feeding and stronger trophic cascades due to suppression of microzooplankton. The feeding rates of mesozooplankton on microzooplankton were not obtained in this study, but the trophic cascades indirectly induced by mesozooplankton carnivorous feeding can be observed by the negative clearance rate on small-sized phytoplankton. Overall, the main significance of this study is the empirical relationship between carnivory degree and clearance rate, which allow researchers to potentially predict the herbivory of mesozooplankton in the nature without conducting feeding experiments.
“…Regression relationships between mortality coefficients of taxon-specific marker pigments and biovolumes of specific grazer size fractions were less impressive, even when significant. For instance, picoplankton mean mortality, computed as the average rate estimates for DVchl a, α-CAR, chl b and ZEAX, was well correlated with total heterotrophs (p < 0.05), but not significantly related to < 5 µm heterotrophic flagellates (R = 0.29, not shown), their likely dominant consumers in nature (Calbet & Landry 1999). In addition, diatom (FUCO) mortality was significantly correlated with biovolumes of > 20 µm CIL and > 20 µm total heterotrophs (R = 0.38, not shown), but neither relationship explained more than 25% of the variability in the grazing rate estimates.…”
Section: Production and Grazing Relationshipsmentioning
confidence: 99%
“…Given an increase in mortality rates of PRO, we would have expected to find a significant relationship with biovolume of small heterotrophic flagellates (Calbet & Landry 1999). The fact that experimental water and samples for < 20 µm protists were usually taken from different hydrocasts may have confounded any underlying relationships, but there could be other factors as well.…”
“…Copepods also both produce Nejstgaard et al Molecular detection fecal pellets that may sediment and are important consumers of sedimenting material (Turner 2002). Copepods may therefore act as key top-down regulators both of the marine plankton food web and of the vertical flux of materials (Verity and Smetacek 1996;Verity 1998;Calbet and Landry 1999;Svensen and Nejstgaard in press). In order to quantify the trophic interactions of copepods and other mesozooplankton in situ, it is not only necessary to assess all important prey, including heterotrophs, but it should also be done with an absolute minimum of handling and temporal and spatial confinement prior to collection and analysis of the predator.…”
The ability to obtain information about feeding selectivity and rates in situ for key organisms such as copepods and other zooplankton is vital for understanding the mechanisms structuring marine ecosystems. Copepods feed on a wide range of prey, and there are presently no methods available to directly quantify zooplankton feeding on all different prey types in situ. Therefore, the development of a new nonintrusive direct method is necessary to gain a better understanding of the trophic interactions in aquatic ecosystems. Molecular methods based on the polymerase chain reaction have recently become an important tool to study predation by arthropods, particularly insects. Here we present the first results of successful molecular detection of a specific prey consumed by calanoid copepods from gut and fecal material. Using the calanoid copepod species Calanus finmarchicus consuming the haptophyte alga Emiliania huxleyi as a model system, 18S ribosomal DNA originating from E. huxleyi was unambiguously detected in whole DNA extracts from copepods and from their fecal pellets. The results also suggest that prey DNA may be quantified for determination of prey-specific zooplankton feeding rates. However, significantly more research under controlled laboratory and field conditions will be required to achieve these objectives. We hypothesize that molecular methods will become an important tool with the potential to quantify undisturbed trophic interactions between individual predators and all their prey in the complex natural plankton.
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