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Population size and structure of three mussel species (Bivalvia ...

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171<br />

Table 2. Analyzed water properties <strong>and</strong> the used measuring<br />

instruments <strong>and</strong> methods<br />

Variable<br />

NO 3 -N, NO 2 -N<br />

NH 4 -N, PO 4 -P<br />

O 2 , temperature<br />

Conductivity<br />

Current velocity<br />

Seston<br />

Instruments <strong>and</strong> methods<br />

Ion chromatograph (Sykam Chromatographie<br />

Vertriebs GmbH)<br />

Photometer Nanocolor 200D (Macherey-<br />

Nagel GmbH)<br />

Oximeter Oxi 96 (WTW)<br />

Conductometer LF 95 (WTW), temperature:<br />

20 °C<br />

Drift body method<br />

Water samples (3 · 1 l) were filtered with<br />

washed (Aqua dest.), dried <strong>and</strong> weighed GF/<br />

C filters (Whatman), after that the filters<br />

were dried (50 °C) <strong>and</strong> re-weighed<br />

water samples were analyzed monthly between<br />

April till October in the years 1996–1999. During<br />

these months, the <strong>mussel</strong>s reach their maximum<br />

activity (e.g. growth, reproduction, metabolism,<br />

translocation) <strong>and</strong> react therefore stronger to<br />

environmental influences.<br />

The concentration <strong>of</strong> oxygen, temperature, <strong>and</strong><br />

current velocity were measured at the sampling<br />

stations. The other variables were analyzed in the<br />

laboratory (Table 2).<br />

To describe the sediment composition at each<br />

station, 15 samples were taken across the width <strong>of</strong><br />

the river using a corer (inner diameter: 55 mm). In<br />

this study, the upper 50 mm <strong>of</strong> the cores were<br />

investigated. The organic content <strong>of</strong> the sediments<br />

was determined by loss on ignition after heating<br />

the samples for 2 h at 550 °C in a muffle furnace.<br />

The percentages <strong>of</strong> s<strong>and</strong>, silt, <strong>and</strong> clay were measured<br />

applying a laser particle <strong>size</strong>r (Fritsch analysette<br />

22).<br />

Survey <strong>of</strong> the <strong>mussel</strong> populations<br />

The samples were taken between 1996 <strong>and</strong> 1998. In<br />

order to secure well-founded data on the abundance<br />

<strong>of</strong> unionids, the entire sediment <strong>of</strong> defined<br />

areas was sieved completely (Haukioja & Hakala,<br />

1974; Hanson et al., 1988; Miller & Payne, 1988,<br />

1993; Amyot & Downing, 1991; Richardson &<br />

Yokley, 1996). Thus, a 0.25 m 2 plastic frame<br />

(quadratic, height: 0.25 m) was pushed into the<br />

substratum. The upper sediment layers within the<br />

frame were removed with a net until more compact<br />

layers, consisting <strong>of</strong> marl, s<strong>and</strong>, or peat, were<br />

reached. The removed material was sieved (4 mm),<br />

<strong>and</strong> the <strong>mussel</strong>s were collected <strong>and</strong> placed in labeled<br />

bags. With the intention to investigate different<br />

ranges <strong>of</strong> the river bed, six <strong>of</strong> those samples<br />

from the bank <strong>and</strong> further six from the middle <strong>of</strong><br />

the river were taken for every sample series. In the<br />

middle <strong>of</strong> the river at station III, samples could not<br />

be taken as described because <strong>of</strong> too s<strong>of</strong>t sediments.<br />

However, areas <strong>of</strong> 0.25 m 2 were investigated<br />

using a dredge closable by a lid in a distance<br />

<strong>of</strong> 5.5–6 m <strong>of</strong>f the bank. The dredged material was<br />

sieved, <strong>and</strong> the <strong>mussel</strong>s were picked out at the<br />

sampling station, too.<br />

There were seven sample series taken at station<br />

I, 3 at station II, <strong>and</strong> 4 at station III. Within one<br />

sampling site, only different areas were investigated<br />

by the several sampling series applying a preestablished<br />

pattern.<br />

In order to ascertain the total <strong>size</strong> <strong>of</strong> the <strong>mussel</strong><br />

populations at every station, four transects were<br />

installed additionally across the river. In every<br />

transect, one sample per meter was taken. The<br />

sampling was carried out as described using frame<br />

<strong>and</strong> net or the dredge, respectively.<br />

The collected <strong>mussel</strong>s were brought to the<br />

laboratory for ageing <strong>and</strong> kept there in a large<br />

vessel filled with river water. The age was identified<br />

by means <strong>of</strong> dark annual rings observed on the<br />

shells (e.g. Haskin, 1954; Crowley, 1957; Negus,<br />

1966; Haukioja & Hakala, 1978; Neves & Moyer,<br />

1988). Difficulties in counting these rings could<br />

appear if <strong>mussel</strong>s stopped their growing after disturbances<br />

<strong>and</strong> formed pseudannuli. Those were<br />

not easily to distinguish from true annual rings.<br />

Furthermore, the age determination could become<br />

difficult if several rings were very close. Such ring<br />

concentrations occurred mainly in the fringe ranges<br />

<strong>of</strong> shells <strong>of</strong> older <strong>mussel</strong>s. Mistakes in the age<br />

determination were avoided by means <strong>of</strong> repeated<br />

controls <strong>and</strong> comparisons <strong>of</strong> shells. After the<br />

investigations, the <strong>mussel</strong>s were released at the<br />

location <strong>of</strong> their origin.<br />

The similarity <strong>of</strong> <strong>species</strong> compositions <strong>and</strong> age<br />

<strong>structure</strong>s ascertained at the sampling stations was<br />

determined using <strong>three</strong> indices. First, for comparing<br />

the presence or absence <strong>of</strong> age classes at the<br />

stations, the set quotient was calculated (Mu¨ ller,<br />

1978, 1987):

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