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The Eurasian Otter Project
Investigations of wild otters (Lutra lutra L.)
in the Nossentiner / Schwinzer Heide national park(Mecklenburg-Western
Pomrania)

Eurasian otter in the otter centre of Hankensbüttel
The Eurasian otter (Lutra lutra L.) is one of the most endangered
mammalian species in Europe. But very little is known about the
otters living conditions and environmental requirements compared
with other large mammal species. The reason for this knowledge deficit
is the relative unsuitability of common wildlife research methods
for otters. Direct otter observation is rare, they are hard to distinguish
visually and difficult to catch or trace by radio- tracking. We
lack information about population density, spatial patterns, reproduction,
causes and proportion of mortality and parameters for habitat quality,
which are necessary for actions in conservation and control of their
success.
We use a new non-invasive method in order to gather fresh data
about free-living otters - avoiding any stress for the animals.
Faecal samples from wild otters can be collected easily as they
are the basis for intraspecific communication. As of recently it
is possible to extract DNA material from faecal samples. Through
genetic analysis we can identify and count the individuals from
our study population, study their spatial movements as well as sex
composition. So we can research otter populations with much better
results than before. In addition we will monitor the numbers of
surviving animals, those found dead and those that have disappeared
in order to assess the influence of road kills and fish traps as
mortality factors.
The nature park "Nossentiner / Schwinzer Heide" (Mecklenburg-Western
Pomerania), is located between Goldberg, Dobbertin, Krakow am See
und Waren on an area of 36.500 ha. There are 60 lakes with an area
of 4.600 ha, 2.370 ha are nature reserve. Two rivers, Nebel and
Mildenitz, flow through several lakes and create a system of habitats
which is attractive not only for otters. Here we defined nearly
200 sample points with periodically control of spraints.

map of our study area with sample points
By microsatellite fingerprinting a DNA profiles of every otter
individual will be established. By means of this database we can
identify the donor animal of new samples.
|
Sample
|
Primer 1
|
Primer 2
|
Primer 3
|
Primer 4
|
Primer 5
|
Animal
|
Sample Site
|
|
94
|
120/
|
120
|
128/
|
128
|
200/
|
204
|
175/
|
187
|
173/
|
177
|
1
|
09.02
|
|
43
|
120/
|
126
|
126/
|
130
|
204/
|
204
|
175/
|
195
|
173/
|
173
|
2
|
13.17
|
|
85
|
120/
|
126
|
126/
|
130
|
204/
|
204
|
175/
|
195
|
173/
|
173
|
2
|
13.17
|
|
19
|
120/
|
126
|
128/
|
128
|
204/
|
204
|
175/
|
195
|
173/
|
173
|
3
|
01.02
|
|
171
|
120/
|
126
|
130/
|
130
|
196/
|
204
|
174/
|
198
|
165/
|
185
|
4
|
04.04
|
|
21
|
120/
|
128
|
130/
|
130
|
196/
|
204
|
175/
|
198
|
165/
|
185
|
5
|
03.01
|
|
81
|
120/
|
132
|
128/
|
130
|
204/
|
208
|
175/
|
195
|
173/
|
173
|
6
|
13.17
|
|
121
|
120/
|
132
|
130/
|
130
|
196/
|
204
|
175/
|
175
|
173/
|
173
|
7
|
13.17
|
|
117
|
124/
|
128
|
130/
|
130
|
196/
|
204
|
199/
|
203
|
173/
|
177
|
8
|
09.15
|
|
90
|
126/
|
132
|
128/
|
130
|
204/
|
208
|
175/
|
195
|
173/
|
173
|
9
|
13.15
|
|
82
|
126/
|
132
|
130/
|
130
|
204/
|
208
|
175/
|
195
|
173/
|
173
|
10
|
13.15
|
|
184
|
128/
|
128
|
124/
|
126
|
196/
|
204
|
175/
|
175
|
165/
|
177
|
11
|
06.01
|
|
3
|
128/
|
128
|
124/
|
134
|
196/
|
200
|
195/
|
203
|
173/
|
185
|
12
|
16.03
|
|
127
|
128/
|
128
|
124/
|
134
|
204/
|
204
|
175/
|
203
|
173/
|
173
|
13
|
17.02
|
|
185
|
128/
|
128
|
128/
|
128
|
196/
|
196
|
175/
|
175
|
165/
|
177
|
14
|
05.02
|
|
181
|
128/
|
128
|
128/
|
128
|
204/
|
204
|
195/
|
195
|
173/
|
177
|
15
|
05.02
|
|
198
|
128/
|
128
|
128/
|
128
|
204/
|
204
|
195/
|
195
|
173/
|
177
|
15
|
05.02
|
|
199
|
128/
|
128
|
128/
|
128
|
204/
|
204
|
195/
|
195
|
173/
|
177
|
15
|
05.02
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DNA profiles of 18 samples from 15 otter individuals
In addition, hormonal pregnancy and stress tests on samples of
individually known otters will follow. Otter carcasses from the
same area were examined for selected diseases and parasites known
to be indicative for a variety of ecological conditions. DNA profiles
of dead otters were compared with those of known animals to investigate
the influence of traffic accidents and fish traps on the mortality
of otter populations. Informations about free-living specimens with
regular occurrence are compared with data of dead found animals.
The combination of all these results will not only increase the
knowledge on habitat use, fitness parameters and causes of death
but would also provide a deeper understanding of ecological requirements
needed for the protection of these highly endangered animals.
During the first four months of our current study we analysed
48 spraint samples of which we identified 32 individuals. Four animals
were resampled three times, five others twice. These results are
useful to analyse time and spatial habitat use. According to the
microsatellite data, marking points were frequented by up to nine
individuals. Allelic pattern retrieved from dead found animals showed
so far no match with already identified animals from the investigation
area.
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