Foundation For Otters
(Alapítvány A Vidrákért) -1156 Budapest, Nyírpalota utca 60.
Report on execution of K+F agreement The national survey of the protected
and endangered otter, numbered 1153/K
1995-1996
I. Introduction
Between November 1995 and March 1996 in Hungary with the co-ordination and
organisation of the Foundation For Otters (Alapítvány A Vidrákért) on behalf of
Departure of Research and Education of Ministry of Environment and Region
Improvement took place the survey of otter (Lutra lutra). Our work has two main
objectives:
1. Getting to know the territorial distribution of Hungarian otter population,
exploring endangering reasons and formulating recommendations for
protecting the species.
2. Real judging of compensating of damages on fishing ponds caused by otters,
establishing the degree and the scale of damages.
This report contains finishing of the task mentioned above in the first point, consistent
and recommendations coming from the results. We have not get particular
commission to judge damages at fishing ponds yet.
II. Background
The number of otters become less frequent in our continent, the continuous
populations became fragmented, and the smaller ones became isolated. At the
conference in Leeuwarden (which was held on discussing the situation of the species
and the possibilities of the protection) on 7-11. June 1994. five more or less isolated
populations were reported:
1. British Islands: United Kingdom and Ireland are very important areas, the
otter is still common, in spite of declining and being rare in most areas of
England.
2. Scandinavia: Otter populations (in the southern part of the countries) are
apparently declining. It would be important to provide connection between
Scandinavian and Northern European areas.
3. Southwest Europe: The Spanish Peninsula and Western part of France are
one of the most important habitats for otter.
4. Central Europe: In Denmark, the Netherlands, Belgium, Luxembourg,
Northern France, Italy, Switzerland, Austria and West part of Germany otter
now became extinct or remains in small isolated populations.
5. Eastern Europe: Russia, Lithuania, Bielorussia, Poland, Eastern parts of
Germany, Czech Republic, Slovakia, Ukraine, Moldavia, Hungary, Romania,
Slovenia, Bosnia, Yugoslavia, Macedonia, Albania, Greece, Turkey. In this
region strong otter populations are still present, but signs of deterioration can
be found.
In the countries of Western Europe attempts are made in order to prevent the further
decline of the species with great amount of financial means and mental energy.
Nowdays the main problems are destruction of habitats, pollution of water and
growing of human disturbance so these problems must be solve first.
Our country has key role in saving the otter, because saving and growing stronger of
stock of otters of Carpathian Basin can be very important condition of surviving of the
species. It burdens us with heavy responsibility financially, morally and professionally.
It is a fact that the most important tasks at present are conservation of suitable
areas, habitats, preservation of populations living there, connecting these populations
through providing ecological/green corridors, stopping illegal chasing. These are
difficult and complex works.
European otter as a species at the top of the food chain is a good indicator of general
health of wetland habitats, therefore any act, which serves the well-being of the
species will act for the benefit for the whole ecosystem including sources used by
humankind (e.g. fish).
It is clear that the species' future depends on how those countries that have wide
spread and developing populations can insure the survival. The decline can be fast and
the strengthening if occurs at all can be very slow. On the other hand forming the
efficient protection need to know the number of otters in the countries, so it is
important to use standardised methods.
Otter is protected in our country since 1974. In the interests of maintaining the
increased protection it is important to get to know the spreading, distribution and
endangering reasons of Hungarian population.
Surveys in the past showed developing population (Nechay G. 1980., Szemethy L.
1990., I. Kemenes - A. Demeter 1994.). Now it was important to repeat the survey,
because the recent social and economical changes touched fundamentally the
property relations. Nowdays the proportion of agricultural areas owned by private
farmers is significant, because 40 percent of the fishing ponds which are important
habitats for otters are belong to private owners. These changes required the survey
and formulating recommendations on the basis of data.
III. Matter and method
The survey was arranged by the method minimum-standard worked out by IUCN. It
was necessary to use that because in Western Europe the same method was used
and therefore the results are comparable with one another (annex I.).
We made a questionnaire (annex II.) arranging the survey and adding the description
of method sent to the following organisations:
- Nemzeti Parki és Természetvédelmi Igazgatóságok (National Park and Nature
Conservation Management)
- Zöld Zala Természetvédelmi Egyesület (Green Zala Nature Conservation
Society)
- Országos Magyar Vadászat Védegylet (National Hungarian Shooting Society
For Promotion)
- Haltermelők Országos Szövetsége (National Association of Fish-Farmers)
- Egyetemes Létezés Természetvédelmi Egyesület Klubja
- Fekete István Környezet- és Természetvédelmi Klub, Mosonmagyaróvár
(Fekete István Environment and Nature Conservation Club, Mosonmagyaróvár)
- Magyar Természetvédők Szövetsége (Association of Hungarian Nature
Conservationists)
The UTM map was provided by Magyar Madártani és Természetvédelmi Egyesület
(Hungarian Ornithological and Nature Conservation Society).
We asked these organisations to support because the Foundation can not cover the
whole country alone during the survey.
We compiled the questionnaire to get the most information from it. We asked to sign
not only the presence or absence of the species but answers on questions needed for
future protection. After receiving and processing data we made UTM standard map
arranged 10x10 km (map).
We noted that data-suppliers could be influenced by subjective reasons and so we did
not get always the real facts. After receiving the answers we controlled 111
questionnaires (from five data-suppliers), and we found that 7 was not correct. While
during the survey period the required information can not be collected with another
method.
IV. The survey and the results
18OO of the questionnaires were sent to the members of the Foundation and to
other observers, 1119 of them had been filled in appreciably, and 34 contained so
little information, that they could not be considered. On the other hand the
questionnaires were filled out in different ways, because some of the questions were
not answered every time.
The types of the areas where the otter has been found were signed in 1087
questionnaires appreciably. The distribution of the otter is showed by the following
marks:
I - permanent
II - not permanent
III - hasn't been found
IV - nor the permanent neither the temporary attendance can be proved
Though the last category was not mentioned in the questionnaires, it was thought to
be written here, because the permanent or temporary attendance in many times
couldn't be proved .
Type of area
| I
| II
| III
| IV
| Total
|
artificial lake
| 205
| 26
| 39
| 11
| 281
|
channel
| 176
| 36
| 42
| 21
| 275
|
river
| 145
| 15
| 11
| 9
| 180
|
stream
| 39
| 21
| 96
| 7
| 163
|
backwater
| 75
| 17
| 14
| 8
| 114
|
natural lake
| 29
| 5
| 3
| 7
| 44
|
water basin
| 18
| 4
| 2
| 6
| 30
|
It is clear that the artificial and natural lakes and the channels were the most frequent
places where the otter was found, after them the rivers (Dráva, Mura, Tisza, Kőrös,
Berettyó, Duna, Sió, Rába, Rábca) and their backwaters. The population is also
stabile in these places. Most of the water basins are also inhabited by the otter, but
footmarks referring to otter weren't registrated near by many of the streams.
In many cases (65) the permanent or temporary attendance wasn't proved, because
marks recognised during the observation couldn't be correctly identified (too old or
blurred), and talking with local inhabitants (verification or denial of the otter's
attendance) wasn't successful.
The permanent attendance of otter was ascertained at most of the artificial and
natural lakes and channels, while the temporary attendance was registrated in less
cases. The fish population of the latter areas isn't present during the whole year, and
the littoral vegetation was mostly plough-land, meadow, pasture.
The population is also stable at rivers, backwaters and waterbasins. The temporary
attendance was registrated those places where river's current is strong, or the river
itself was polluted, and the littoral vegetation is lacking or scattered.
Near those streams, where the otter is permanent there are generally areas
abounding in fish or the stream itself supplies the otter with fish. These conditions
aren't given in places where provisionary attendance was registrated. The lack of
littoral vegetation and considerably human disturbation can be mentioned as reasons
as well.
Lakes not visited by otters at all are mostly angler-lakes with embanked shore
generally. These areas in most of the cases aren't covered by plants and deserted
without considerable population of fish.
The parts of the channels, waterbasins, rivers and streams where the otter wasn't
found are either disturbed (close to settlement, regular human motion), or polluted,
the rivers' current are too strong, the fish population is missing totally, and lacking of
the littoral vegetation is conspicious.
It is ought to be mentioned, that human disturbance is responsible in the smallest
degree for the otter's disturbance, the observers met otters many times near by
human settlements, and the attendance is not temporary there as well (for example
animals regularly visit towns like Kaposvár, Szigetvár).The most important reasons
for temporary attendance are:
- pollution of water
- food supply is not suitable
- bankside vegetation is lacking
Answers returned from each county by and the types of areas are the following:
0 - no information
I - natural lake
II - artificial lake
III - river
IV - channel
V - waterbasin
VI - stream
VII - backwater
T - total
County
| 0
| I
| II
| III
| IV
| V
| VI
| VII
| T
|
Szabolcs
| 0
| 1
| 16
| 76
| 27
| 1
| 0
| 80
| 201
|
Hajdú
| 5
| 0
| 42
| 21
| 65
| 1
| 0
| 1
| 155
|
Somogy
| 7
| 3
| 63
| 7
| 32
| 2
| 29
| 3
| 146
|
Pest
| 4
| 3
| 36
| 20
| 3
| 5
| 48
| 2
| 121
|
Baranya
| 7
| 3
| 30
| 2
| 36
| 8
| 20
| 0
| 106
|
Zala
| 1
| 7
| 31
| 6
| 4
| 3
| 18
| 4
| 74
|
Veszprém
| 1
| 6
| 16
| 2
| 6
| 1
| 39
| 0
| 71
|
Csongrád
| 0
| 6
| 6
| 11
| 18
| 4
| 0
| 2
| 47
|
Bács
| 0
| 4
| 3
| 4
| 21
| 0
| 0
| 5
| 37
|
Fejér
| 0
| 2
| 12
| 7
| 16
| 0
| 0
| 0
| 37
|
Szolnok
| 5
| 1
| 5
| 4
| 9
| 4
| 0
| 0
| 28
|
Tolna
| 0
| 0
| 3
| 3
| 7
| 0
| 0
| 7
| 20
|
Vas
| 0
| 2
| 7
| 3
| 0
| 0
| 6
| 1
| 19
|
Békés
| 0
| 4
| 3
| 4
| 2
| 0
| 0
| 5
| 18
|
Győr-Sopron
| 0
| 0
| 1
| 6
| 8
| 0
| 0
| 0
| 15
|
Borsod
| 0
| 0
| 0
| 3
| 0
| 1
| 0
| 4
| 8
|
Heves
| 0
| 1
| 1
| 1
| 1
| 0
| 2
| 0
| 6
|
Komárom
| 0
| 0
| 5
| 0
| 0
| 0
| 0
| 0
| 5
|
Nógrád
| 2
| 1
| 1
| 0
| 0
| 0
| 1
| 0
| 5
|
Total
| 32
| 44
| 281
| 180
| 275
| 30
| 163
| 114
| 1119
|
This table shows that the attendance of otter is most frequent in the south-west and
west part and the east and south-east part of the country, and perceptible in the
north-west part of the Dunántúl- Transdanubian region, Mezőföld, and areas between
the Danube and Tisza.
No otter was found in the Northern mountains.
Survey in Kisalföld show this species appears in Szigetköz region again. We have
few data from county of Nógrád, Heves, Komárom and Borsod.
Though the otter often attends near fish ponds in the Dunántúl - Transdanubian region
(it doesn't mean that rivers and channels aren't visited by this animal), in other parts of
the country this type of area wasn't the most frequent one, though lakes have great
importance.
Processing data about the bankside vegetation had the following results (1001
appreciable answers were sent back):
Bankside vegetation
| Frequency
|
reed and sedge together
| 470
|
forest
| 91
|
reed
| 120
|
sedge
| 97
|
meadow
| 79
|
other (pasture, plough-land)
| 44
|
Together
| 1001
|
It is apparent, that otter prefers reed-sledge vegetation but can be found in areas
covered only by reed, and in forests near the shores. These places are thick and well-
covered, so the otter can hide in and make nests. In the other cases the otter could
be registered only if there was thick vegetation near by.
The questionnaires' results shows that the animal attends in 908 areas, where
attendance can be told as:
-permanent in 649 areas
-eventually otter may appear in 176 areas
-can't be decided if the attendance is permanent or temporary in 83 areas
(We recognised these areas as temporary ones.)
-wasn't found in 211 areas
717 appreciable answers referring to marks of otters were sent back.
Marks
| Number of perception
|
many types of marks
| 416
|
footmarks
| 106
|
remains of fish
| 89
|
spraints
| 64
|
dead otter
| 11
|
living otter
| 31
|
Total
| 717
|
The simultaneous traces, indicated from 416 sites, were:
- footmarks and spraints 276 times
- footmarks with fish remains 56 times
- fish remains and spraints 27 times
- all three of the above 57 times
During the survey we could generally record several otter-indicating, species-
characteristic traces. Registering a singular trace is also current; however it is to be
noted that in case of recording fish remains or droppings as a singular trace, we
emphasised repeated checking (and asked the surveyors to act accordingly), as
other species may produce similar traces. This was important because in such cases,
the probability of a mistake or misjudgement is relatively high.
Unfortunately in the case of fallen otters, the surveyors did not give more information
than registering the dead animals. Only four records were made about the cause of
death: three otters were reported to have been crashed by cars; one was killed by
foxes.
Living otters were mostly seen at dawn and late in the evening, generally by wildlife
guards and hunters. On eight occasions they were observed by daylight: on the ice
(four times) or on the river bank (three times). Once (in January 1996) three otters were
seen together; probably a female with the cubs.
We have 861 records of the weather during observations:
Weather
| How many times
|
snowy
| 576
|
sunny
| 165
|
rainy
| 16
|
other (fog, snow-storm, thunder-storm)
| 104
|
In all
| 861
|
Observation was much facilitated by snowy weather, for then it is easier to register
traces. Also many records were made in sunny weather, though a great majority
(147) of such cases consisted of inspection of snow-covered sites. As the probability
of false records is high in rainy or very heavy weather, the given area was repeatedly
checked under similar conditions.
The following appraisal responses arrived concerning the way (I) and site (II) of
observation.
| Observation
| No of times
|
I
| from vehicle
| 0
|
| scouting
| 576
|
| from a post
| 5 (living otters)
|
| other
| 17
|
II
| on dams
| 372
|
| near water
| 528
|
| under bridge
| 404
|
| other
| 8
|
Analysing the above answers shows that most observations were made:
- scouting near water 2O2
- scouting on dams 117
- scouting under bridges 1O1
- scouting near water, on dams
and under bridges at the same time 8O
- scouting under bridges and on dams 76
- scouting near water, under bridges 147
- scouting near water on dams 99 cases.
It is apparent that otters show a preference for leaving traces under bridges and on
dams, since the result obtained other than by was of scouting (that is, those
concentrated specifically on an under-bridge area or a dam part) indicate 156 times
the presence of otters.
The five otters seen from a post, were observed by professional hunters or wild-life-
guards.
V. Conclusions
It could be inferred that otters populate mostly areas with ample food supplies where
the vegetation is sufficiently dense to provide shelter and nesting facilities for them. In
areas with insufficient food supplies (i.e. areas where fish are scarce or missing) and
little or no coastal vegetation otters appear only occasionally and do not settle down
permanently. They prefer reed-sedge vegetation and also like dense coastal forests,
forest patches and coastal bush vegetation. It is important -especially in the case of
fish farms and ponds maintained for sports- to preserve coastal and aquatic
vegetation as its destruction may also lead to the disappearance of otters from the
area. If appropriate lairs are available otters even tolerate strong disturbance and do
not leave the region. Otters are very adaptable - they regularly enter even inhabited
areas if it feels safe (e.g. in the region of Szigetvár, Kaposvár).
In the case of rivers and streams also water pollution may cause a problem apart
from insufficient food supplies and the lack of coastal vegetation.
Despite all the aforementioned problems the population of otters in Hungary seems to
be stable and growing. Yet the recent changes in ownership of land and the closely
related increase of illegal killing (hunting, trapping, etc.) of otters may cause
irreparable damage.
The study has shown clearly that most problems arise in the neighbourhood of fish
farms. From these regions -where the presence of otters is known- more claims for
damages have been made.
We have to point out, however, that the study was conducted in winter when otters
visit the neighbourhood of fish farms more frequently. Most of the damage is, hence,
concentrated to the wintering facilities and in the other seasons the presence of otters
goes often completely unnoticed. That is why most claims from the neighbourhood of
fish farms are made in winter while claims in other seasons are negligible compared
to these.
We must also see that in many cases it is the animals (mammals, birds) living there
that managers of fish-ponds hold responsible for low profits. This seems a forced
effort to explain low profits and the inappropriate management by the people and
organisations working at the ponds. It is also a fact that the locals have voiced their
dislike of the present regulation which rules that they receive no compensation for
damage done by an animal under protection. At the present the processing of
compensation claims (shooting claims) is a slow, hard procedure, this is also a reason
why part of the fish-pond managers are not co-operative with the nature protection
authorities.
We should like to point out that compensation is not the only way though we think it is
clearly advisable for the protection of this species in the future. Instead, the otter
should be incorporated into the management of fish-ponds, through stimulating
system that allows the "damage" coming from the otters presence and lifestyle to be
the part of the economy and the management.
We can see that, according to locals, it is an unwanted visitor at the fish ponds where
its presence is known. Also, in the present the species is clearly (though illegally, but
more or less openly) hunted around the lakes, which is already a serious problem for
the environmentalists today and maybe in the future.
We must also note that the damage it does and being hunted are not closely linked.
We can observe that it's hunted at lakes where it is said to do minimal damage, and
that in places where unbearable damage has been reported, it is left alone. In several
cases the reason for its killing is tradition: for there are deeply rooted traditions alive
even today, and capture, trapping and killing animals (otters, among them) is one of
them. Also, it is fashionable to kill otters one is to have otter skin, pelt, even if there is
no profit from it at all. Therefore, damage can definitely not be considered the prime
reason for its hunt.
VI. Recommendations
- Suppressing the illegal hunting of the otter in the area of fish ponds by
estimating and measuring the veracity of the compensation claims and by
giving partial or full compensation for the damages caused by otters.
- Creating economic regulations which could make possible that the damage
costs caused by otters would be compensated through tax and credit relieves.
- Checking regularly the feeding habits of the otter which is a very important tool
in deciding about the veracity of compensation claims for damages caused by
otters.
- Moving otters from a dangerous territory to such habitat where all the
important conditions are insured for them (preferably nationally protected
areas). It should be supported by a serious preparatory (ethological, ecological
and genetic research) and implementation studies.
- Examining those areas which have not been checked before and making
comprehensive studies on it.
- Supporting research works which aim to examine the connections between the
occurrence of otters and water pollution or the vegetation types of the different
fresh-water ecosystems.
References
- Convention on the Conservation of European Wildlife and Natural Habitats
(1994): Seminar on the Conservation of the European Otter (Lutra lutra) -
Leeuwarden, Nederland
- Nechay, G. (1980): Die Situation der Fischotter in Ungarn; p. 215-221. Ex.
Reuter & C. Antal, F. : Der Fischotter in Europa, Oderhaus, Göttingen.
- Szementhy, L. (1990): Egyes védett ragadozók elterjedése Magyarországon.
Agrártudományi Egyetem Vadbiológiai Kutató, Gödöllő.
- I. Kemenes & A. Demeter (1994): Uni- and miltivariate analysis of the effects of
environmental factors on the occurance of otters (Lutra lutra) in Hungary.
Annales Historico, Maturales Musei Nationalis Hungarici, p. 133-138.
Annex I.
The aim, principles and methods of a national otter survey.
Aim:
To investigate the spatial/territorial distribution of the otter (Lutra lutra) therefore to
get an estimation about the national otter population.
Basic principles:
The presence of the otter can be fairly easily and certainly recognised in a given
habitat on the basis of foot-marks, droppings and other characteristics, so called
otter-signs/marks. However making a quantitative survey is extremely difficult
because more than one individuals can use regularly the same trap. Because the otter
always lives near water courses, it is easy to determine its habitat on a larger
scale?/area. The presence of the otter can be marked by carrying out a survey on the
already determined large habitat or on parts of it. Therefore a survey only shows the
presence or the absence of the otter, however, it is also advisable to record if there
has been seen signs of only (probably) one otter or many otters (e.g. many foot-
marks of different sizes); or that there has been plenty of marks/signs seen.
Methods:
The methods of otter survey is uniform in all over Europe. A minimum of 600 metres
section of a given territory should be thoroughly examined. It means that e. g. the
section of this size should be looked through on river-bank and only after doing so,
can be declared the presence or the absence of the otter. If there are otter-signs on
the first ten metres section, there is no need to continue the survey on the remaining
of the whole section. It can already be concluded that this survey point is used by the
otter. It complies to other survey points as well. Survey points which should be
examined by all means: water courses flowing under roads (bridges), dams between
lakes or water-reservoirs.
If it is not possible to examine a 600 metres section because of the shortness of a
dam, the survey should be continued on the neighbouring dams or river banks and
lake shores. If the lake is so small that even the last mentioned survey method is
impossible to be carried out, then the survey should be continued on the banks of the
incoming or outgoing water-courses/flows.
The survey can be carried out in any time of the year, however, it is very difficult to be
done in the months of lush vegetation (from May to October) and the possibility of
making mistakes is also higher in this period. Therefore the surveys should be done
from October to end of March.
Recording the time of survey and the characteristics of the territory is very important.
If there are no typical characteristics of a given territory the person making the survey
may need to create some.
Annex II.
Questionnaire for a National Otter Survey
Please answer only those questions to which you can give a sure answer.
Please send the filled out questionnaire to the address of the "Otter Foundation or
Foundation for the Otters" ( 1156. Budapest, Nyirpalota utca 60.) until 30th of March
1996.
Thank you very much for your help.
Name:
Address:
Time of survey:
1. County:
1.1. Nearest settlements:
1.2. The area where the otter has been seen/observed:
1.3. The size of the area where the otter has been observed/seen, and the
proportions of surface-water:
1.4. Characteristics of the area:
- natural or artificial lake
- river
- channel
- water-reservoir
- other
1.5. Riparian vegetation type:
- reeds
- rush
- meadow
- forest
- other
2. Result of the survey:
- presence of otter(s)
- absence
2.1. Is the presence of otters permanent?
- yes
- no
2.2. Observed signs of otters:
- footmarks
- remains of fish
- spraint
- dead otters
- other
2.3. Wheather-conditions during the observation:
- rainy
- snowy
- sunny
- other
2.4. Other conditions of the observation:
- sitting on a vehicle -standing on a dam
- stalking -on river-bank or lake-shore
- sitting -under the bridge
- other -other
2.5. Local people's opinion about the otter
2.6. Other information relevant to the survey:
Result of the 1995-1996 Hungarian otter survey