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School of Engineering and Science - Jacobs University

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CHAPTER I<br />

Maximum values always occurred during the summer months (June-August) when<br />

Noctiluca scintillans, Gyrodinium spp. <strong>and</strong> Protoperidinium spp. occurred together.<br />

Towards winter in t<strong>and</strong>em with decreasing chlorophyll a concentrations, heterotrophic<br />

din<strong>of</strong>lagellate biomass reached its minimum suggesting close coupling with its<br />

phytoplankton food. Outliers in biomass <strong>of</strong> heterotrophic din<strong>of</strong>lagellates in December<br />

2007 <strong>and</strong> January 2008 stem from the presence <strong>of</strong> single cells <strong>of</strong> N. scintillans. During<br />

the investigation period mixotrophic din<strong>of</strong>lagellates (Figure 2) usually played a minor<br />

role compared to heterotrophic species (0.3–30 µgC L -1 ). Only in summer 2007 did they<br />

form an intense bloom from the end <strong>of</strong> July to mid <strong>of</strong> October thereby exceeding the<br />

biomass <strong>of</strong> heterotrophic din<strong>of</strong>lagellates by far (Figure 2). The bloom was first<br />

composed mainly <strong>of</strong> Lepidodinium chlorophorum as well as Scrippsiella sp. <strong>and</strong><br />

Prorocentrum triestinum in lower densities. From mid September onwards the bloom<br />

comprised mainly Akashiwo sanguinea. During the rest <strong>of</strong> the sampling period<br />

mixotrophic din<strong>of</strong>lagellates were usually present in much lower concentrations than<br />

heterotrophic ones.<br />

The ciliates found comprised 63 taxa. As mentioned above ciliates were considered<br />

heterotrophic, with the exception <strong>of</strong> Myrionecta rubra, <strong>and</strong> were grouped together for<br />

illustration (Figure 3). Ciliated protozoa were present throughout the time <strong>of</strong> monitoring<br />

with concentrations varying between 0.2 <strong>and</strong> 106 µgC L -1 . In terms <strong>of</strong> biomass,<br />

strombidiids played the most important role during the monitoring program, followed<br />

by M. rubra <strong>and</strong> then haptorid <strong>and</strong> strobilid ciliates (Figure 1, right panel). Tintinnids<br />

<strong>and</strong> prostomatid ciliates as well as other ciliates were only <strong>of</strong> minor importance. Ciliates<br />

showed a different succession pattern when compared with din<strong>of</strong>lagellates. Although<br />

they also followed the development <strong>of</strong> chlorophyll a in spring they responded with an<br />

earlier <strong>and</strong> steeper increase to enhanced food availability (Figure 3). Maxima were<br />

again found earlier in the year (March-early June) compared to din<strong>of</strong>lagellates <strong>and</strong><br />

mainly comprised Strombidium spp. <strong>and</strong> Cyclotrichium spp.. During the summer<br />

months ciliate biomass fluctuated synchronized with chlorophyll a concentration.<br />

Towards winter it also decreased parallel with declining chlorophyll a concentrations.<br />

The species M. rubra gained in importance during late spring <strong>and</strong> summer where it<br />

sometimes surpassed the biomass <strong>of</strong> the residual ciliates. Maximum concentrations <strong>of</strong><br />

this ciliate (97 µgC L -1 ) were found in June 2009.<br />

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