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School of Engineering and Science - Jacobs University

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CHAPTER III<br />

in words <strong>and</strong> deeds. Many thanks to the technical department <strong>of</strong> the BAH for all the<br />

perfect “short notice” solutions <strong>and</strong> to Arne Malzahn for his technical support. Special<br />

thanks also to the “Copepod Hunter” Katherina Schoo for catching <strong>and</strong> sorting out all<br />

the copepods for our experiments. Furthermore thanks to the crews <strong>of</strong> the research<br />

vessels Uthörn <strong>and</strong> Aade, Kristine Carstens, Silvia Janisch <strong>and</strong> last but not least the<br />

whole team <strong>of</strong> the AWI Food Web Project.<br />

APPENDIX<br />

Table 1: Microzooplankton grazing g [d -1 ] <strong>and</strong> phytoplankton growth rates k [d -1 ] determined in four<br />

dilution experiments for each prey category. Food saturation marked with gray background. Instantaneous<br />

growth rate values µ 0 [d -1 ] from bottles without added nutrients. Percentage <strong>of</strong> initial stock P i [%] <strong>and</strong><br />

potential production grazed P p [%]. Negative P i <strong>and</strong> P p values resulting from negative g (P i ) or µ 0 (P p )<br />

<strong>and</strong> were set to zero. The same was done for positive P p values resulting from negative g <strong>and</strong> µ 0 . MMC =<br />

mean microzooplankton carbon biomass. P-values from linear regression analysis <strong>of</strong> apparent<br />

phytoplankton growth against dilution factor (n = 36). * p < 0.05, ** p < 0.01, *** p < 0.001, **** p <<br />

0.0001.<br />

Table 2: Microzooplankton carbon specific filtration rates F c [L µgC predator -1 d -1 ] <strong>and</strong> carbon specific<br />

ingestion rates I c [µgC prey µgC predator -1 d -1 ], total filtration rates F [L d -1 ], total ingestion rates I [µgC<br />

prey L -1 d -1 ] <strong>and</strong> electivity E* [-] for each prey category. Positive selection marked with gray background.<br />

MMC = mean microzooplankton carbon biomass. P-values are the same as for the grazing rates <strong>of</strong><br />

microzooplankton. * p < 0.05, ** p < 0.01, *** p < 0.001, **** p < 0.0001.<br />

Table 3 a+b: Temora longicornis grazing g [d -1 ], phytoplankton <strong>and</strong> microzooplankton growth rates k<br />

[d -1 ] determined in four grazing experiments for each prey category. Instantaneous growth rate values µ 0<br />

[d -1 ] from dilution experiment bottles without added nutrients. Percentage <strong>of</strong> initial stock P i [%] <strong>and</strong><br />

potential production grazed P p [%]. Negative P i <strong>and</strong> P p values resulting from negative g (P i ) or µ 0 /k (P p )<br />

were set to zero. The same was done for positive P p values resulting from negative g <strong>and</strong> µ 0 /k. TC = Total<br />

T. longicornis carbon biomass. P-values derived from t-tests against zero.* p < 0.05, ** p < 0.01, *** p <<br />

0.001, **** p < 0.0001.<br />

Table 4 a+b: Temora longicornis carbon specific filtration rates F c [L µgC predator -1 d -1 ] <strong>and</strong> carbon<br />

specific ingestion rates I c [µgC prey µgC predator -1 d -1 ], total filtration rates F [L d -1 ], total ingestion rates<br />

I [µgC prey L -1 d -1 ] <strong>and</strong> electivity E* [-] for each prey category. Positive selection marked with gray<br />

background. TC = Total T. longicornis carbon biomass. P-values derived from t-tests against zero.* p <<br />

0.05, ** p < 0.01, *** p < 0.001, **** p < 0.0001.<br />

94

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