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Náttúrufræðingurinn - 1997, Síða 12

Náttúrufræðingurinn - 1997, Síða 12
Lindström, J., E. Ranta, V. Kaitala & H. Lindén 1995. The clockwork of Finnish tetraonid population dynamics. Oikos 74. 188-194. Ólafur K. Nielsen 1995a. Rjúpnamerkingar. Bliki 15. 63-66. Ólafur K. Nielsen 1995b. Rjúpnatalningar á Norðausturlandi 1981 til 1994. Náttúru- fræðingurinn 65. 165-179. Ólafur K. Nielsen & Gunnlaugur Pétursson 1995. Population fluctuations of Gyrfalcon and Rock Ptarmigan: analysis of export fig- ures from Iceland. Wildlife Biology 1. 65- ' 71. Ævar Petersen 1991. Rjúpur og rjúpnaveiðar. Sportveiðiblaðið 10. 74-78. ■ SUMMARY ROCK PTARMIGAN STUDIES AT KVÍSKER, SOUTHEAST ICELAND 1963 TO 1995 The Icelandic Rock Ptarmigan (Lagopus mutus) population fluctuates in size and ca. 10 years have been between peak years (Finnur Guðmundsson 1960, Amþór Garðarsson 1988, Ólafur K. Nielsen and Gunnlaugur Pétursson 1995). To monitor population changes territo- rial cocks (Fig. 1) are counted each spring on selected plots in different parts of the country. The purpose of this paper is to report the re- sults of ptarmigan censuses and banding at Kvísker (63°59’N, 16°26’W) in SE-Iceland (Fig. 2). The total area of the ptarmigan study plot is 2.1 km2, and it is located on a south fac- ing slope on the foothills of the great glacier Vatnajökull. The farm Kvísker is within the study plot. The lower edge of the plot is at 30 m above sea level and the upper edge is at 120 m. The characteristic vegetation is birch scmb (Betula pubescens) and open areas with heathland vegetation such as Empetrum nigr- um, Vaccinium uliginosum and Racomitrium lanuginosum. Territorial cocks were censused once each year in the period 12 to 20 May. The census was timed so as to be over before folia- tion of the birch scmbs, and was always com- pleted in one day. In some years more than one spring census was conducted and the count giv- ing the highest figures was used. Ptarmigan were caught for banding at Kvísker by driving them into corrals or by snaring them, using stuffed birds as decoys (for cocks in spring) (Ólafur K. Nielsen 1995a). All censuses and banding has been done by the same person (Hálfdán Bjömsson), who also made all but seven of the recoveries and all of the controls. In the period 1963 to 1995 the average number of territorial cocks was 20.5 (9.8 cocks/km2). The maximum fígure was 53 cocks (25 cocks/km2) and the minimum 7 cocks (3.3 cocks/km2). The difference in numbers be- tween the highest and the lowest year was ap- proximately 8-fold. Population trends are shown in Fig. 3. There was a clear peak in numbers in 1966. Following low years in 1970 and 1971 the population increased to medium density levels in the early 1970s and remained at such levels for 10 years. This was followed by a decrease starting in the mid 1980s and reaching a low in 1991 and 1992 and then again an increase. Compared with 7 ptarmigan census plots in N- and NE-Iceland the Kvísker plot ranks among the denser ones, being surpassed only by Hóll on Tjömes (Ólafur K. Nielsen 1995b) and Hrísey (Ævar Petersen 1991). On Hrísey density was 41 cocks/km2 during a peak year (Ævar Petersen 1991). Comparing population trends for Kvísker, Hrísey and six plots in NE- Iceland we found that all areas behave more or less in the same fashion with regard to changes in numbers (Fig. 4). A total of 916 ptarmigan had been banded at Kvísker at the end of the year 1995. This in- cluded mostly young of the year (juve- niles,753), but also adult hens (91), cocks (64) and unsexed full-grown birds (8). Fifty-one ptarmigan (6%) have been recovered dead. The most common cause of death was collisions with barbed wire fences or overhead wires (Fig. 5). The recoveries give a biased picture of death causes, as birds killed by predators are underestimated and importance of collisions and hunting is overestimated. Sixty controls of ringed ptarmigan have been made and all at Kvísker. Thirty-four adults of 155 banded (21%) were recovered or control- led at Kvísker but only 70 (9%) of 753 juve- niles. This difference between age groups is significant (chi-square=14.137, p«0.001), and probably reflects both juvenile dispersal and higher mortality of juveniles during fírst winter as compared with adults. Juveniles are banded in late summer and most recoveries and controls are made the following spring and summer but few during the preceding winter when most of the mortality takes place. Thirty-four ptarmigan banded as juveniles 122
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