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10 results for “tropical zooplankton”
Fig. 1 in The Composition, Diversity And Community Dynamics Of Limnetic Zooplankton In A Tropical Caldera Lake (Lake Taal, Philippines)
Fig. 1. Map of Lake Taal with the six sampling sites (NB – North Basin, SB – South Basin). The insert shows the location of Lake Taal and the other lakes mentioned in the text (P – Lake Paoay, Lb – Lake Laguna de Bay, N – Lake Naujan and Ln – Lake Lanao).
Fig. 4 in The Composition, Diversity And Community Dynamics Of Limnetic Zooplankton In A Tropical Caldera Lake (Lake Taal, Philippines)
Fig. 4. Monthly variations in Shannon-Wiener Diversity (H') Index values of rotifers and cladocerans in the north and south basins of Lake Taal.
Fig. 3 in The Composition, Diversity And Community Dynamics Of Limnetic Zooplankton In A Tropical Caldera Lake (Lake Taal, Philippines)
Fig. 3. Mean monthly biomass (μg / l) of common zooplankton species from the north and south basins of Lake Taal for the year 2008.
Fig. 5 in Top-Down Control Of Phytoplankton By Zooplankton In Tropical Reservoirs In Singapore?
Fig. 5. The correlations of cladocerans with phytoplankton genera with high loadings on PC3; i.e. Anabaena, Dictyosphaerium, Melosira and "other cyanobacteria" (see Table 3). Cladoceran counts were expressed in number per m3 while phytoplankton counts were expressed as number per ml3.
Fig. 4 in Top-Down Control Of Phytoplankton By Zooplankton In Tropical Reservoirs In Singapore?
Fig. 4. The correlations of rotifers with phytoplankton genera with high loadings on PC1 and PC2; i.e. Ankistrodesmus, Cosmarium, Melosira, Peridinium, Planktotrix sp. 1 and 2, Scenedesmus, Synedra and Trachelomonas (see Table 3). Rotifer counts were expressed in number per m3 while phytoplankton counts were expressed as number per ml3.
Fig. 3 in Top-Down Control Of Phytoplankton By Zooplankton In Tropical Reservoirs In Singapore?
Fig. 3. The correlations of cyclopoid copepods with phytoplankton genera with high loadings on PC1 and PC2; i.e. Ankistrodesmus, Cosmarium, Melosira, Peridinium, Planktotrix sp. 1 and 2, Scenedesmus, Synedra and Trachelomonas (see Table 3). Cyclopoid counts were expressed in number per m3 while phytoplankton counts were expressed as number per ml3.
Fig. 2 in Top-Down Control Of Phytoplankton By Zooplankton In Tropical Reservoirs In Singapore?
Fig. 2. The correlations of calanoid copepods with phytoplankton genera with high loadings on PC1 and PC2; i.e. Ankistrodesmus, Cosmarium, Melosira, Peridinium, Planktotrix sp. 1 and 2, Scenedesmus, Synedra and Trachelomonas (see Table 3). Calanoid counts were expressed in number per m3 while phytoplankton counts were expressed as number per ml3.
Fig. 1 in Top-Down Control Of Phytoplankton By Zooplankton In Tropical Reservoirs In Singapore?
Fig. 1. Location of reservoirs within Singapore within which zooplankton and phytoplankton samples were monitored every month between 1992 and 2006. 1. Bedok, 2. Lower Seletar, 3. Upper Seletar, 4. Lower Peirce, 5. Upper Peirce, 6. MacRitchie, 7. Kranji, 8. Pandan, 9. Jurong Lake, 10. Murai, 11. Poyan and 12. Tengeh.
Fig. 2 in The Composition, Diversity And Community Dynamics Of Limnetic Zooplankton In A Tropical Caldera Lake (Lake Taal, Philippines)
Fig. 2. Average abundance (Ind. / l) and number of species of Copepoda, Cladocera and Rotifera from the upper 40 m in Lake Taal in the year 2008. The Copepoda were grouped into nauplii, Calanoida and Cyclopoida.
Is zooplankton body size an indicator of water quality in (sub)tropical reservoirs in China?
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