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