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School of Engineering and Science - Jacobs University

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DISCUSSION<br />

<strong>and</strong> showed a clear seasonality with minima during winter <strong>and</strong> maxima during summer.<br />

The heterotrophic part <strong>of</strong> both groups contributed to the planktonic biomass with carbon<br />

concentrations ranging from 2 to 652 µg L -1 . Including also mixotrophic species yielded<br />

maxima <strong>of</strong> 779 µg L -1 . These concentrations are in a typical range for the North Sea<br />

(Riegman et al., 1993, Brussaard et al., 1995).<br />

The community I observed was highly diverse, with 62 din<strong>of</strong>lagellate taxa <strong>and</strong> 63 ciliate<br />

taxa typical for the North Sea (Riegman et al., 1993, Brussaard et al., 1995, Hoppenrath,<br />

2004, Stelfox-Widdicombe et al., 2004). The numerically most important heterotrophic<br />

din<strong>of</strong>lagellates were species <strong>of</strong> the genera Gyrodinium <strong>and</strong> Protoperidinium, while<br />

Noctiluca scintillans contributed large proportions to the biomass. Mixotrophic<br />

din<strong>of</strong>lagellates <strong>of</strong> several genera partly also reached a high planktonic biomass during<br />

blooms. The most important ciliates, in terms <strong>of</strong> abundance, were species <strong>of</strong> the genera<br />

Strombidium <strong>and</strong> Strobilidium, the functionally phototrophic Myrionecta rubra <strong>and</strong><br />

tintinnids. Large Cyclotrichium spp. contributed substantially to ciliate biomass. The<br />

data on ciliates presented in Chapter 1 are completely new for Helgol<strong>and</strong> Roads,<br />

whereas din<strong>of</strong>lagellates have been counted since 1962 (Wiltshire & Dürselen, 2004).<br />

However, these records do not mirror the natural diversity (Hoppenrath, 2004). My<br />

monitoring aimed at a higher taxonomic resolution in din<strong>of</strong>lagellates <strong>and</strong> ciliates<br />

compared to the Helgol<strong>and</strong> time series on plankton. This could partially be achieved<br />

(Chapter I) (Protoperidinium spp., ciliates). The longer monitoring period compared to<br />

other studies (Riegman et al., 1993, Brussaard et al., 1995, Stelfox-Widdicombe et al.,<br />

2004) also revealed general patterns in the seasonality <strong>of</strong> both groups.<br />

However, there is still a great need for further work on this topic at Helgol<strong>and</strong> Roads<br />

<strong>and</strong> a microzooplankton monitoring aiming at a higher taxonomic resolution should be<br />

included into the long-term observation for detailed insights into the species<br />

composition. Due to the methodology used (Lugol fixation <strong>and</strong> light microscopy) many<br />

cells could be identified to genus level only or were assigned to morphologically similar<br />

groups (Johansson et al., 2004). Especially naked ciliates <strong>and</strong> din<strong>of</strong>lagellates should<br />

receive further attention. Elucidating the taxonomy <strong>of</strong> these groups by applying live<br />

observation, epifluorescence (Elbrächter, 1994, Kraberg et al., 2010) <strong>and</strong> scanning<br />

microscopy techniques (Hern<strong>and</strong>ez-Becerril et al., 2010), as well as staining techniques<br />

(Agatha & Tsai, 2008) is feasible. Applying these methods in combination with<br />

molecular methods (Sherr & Sherr, 2002) provides further insights into the taxonomy <strong>of</strong><br />

din<strong>of</strong>lagellates (Gottschling et al., 2005) <strong>and</strong> ciliates (Agatha, 2004). For gaining<br />

fundamental knowledge on the role <strong>of</strong> microzooplankton in the food web we first have<br />

127

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