Abstract

Harbour seals (Phoca vitulina) have been harvested in Iceland since the first settlers arrived in the 9th century. Pups were generally netted, clubbed and harpooned until 1875 when general use of guns for hunting began. Seal-hunting has been traditional amongst the farms legal rights. Seal hunting was an important supplement to other economic resources. Harbour seal skins, salted ordried, were exported and large dataset of catch statistics is available from trading logbooks since the late 19th century. In the early 20th century catch was about 6,000. In the ‘bounty’ period 1982 – 1989, maximum catches were of 4,000 animals with about 350 hunters participated; in 2006 catches were only about 100 animals with 18 hunters. After 1989 the population continued to decline even though catches decreased markedly. Unreported by-catch in fishing gear, hunt for local consumption and shooting of seals swimming in salmon rivers estuaries may have kept the total removal from the stock above sustainable levels. A considerable Icelandic knowledge base had been compiled about the biology of the harbour seal since the late 16th century, with the first written reference in 1588-1589. In the last decades, research on various aspects of its biology and monitoring have been intensified, with focus on abundance, distribution, diet and nematode infestation. The main results show that the Icelandic harbour seal population - has declined annually about 5% in the period 1980-2006, - was most abundant on the NW-coast, - feeds mainly on sand-eels and gadoids, - and was less infected with anisakid nematodes than grey seals. Seal watching, as a low-consumptive indirect utilization, may represent a new economical opportunity if properly regulated.

Highlights

  • In the 9th century, when Iceland was settled there is indication of large abundance of seals and many locations are named after seals and sealing (Kristjánsson 1980, Hallgrímsson 1985)

  • The fishing is mainly conducted in the period from March to June in shallow waters and the fishing effort is quite variable and fluctuates inter-annually with the demand for roe on fishing markets. It peaked in mid 1980’s and 1990’s but has been relatively low since 1997 (MRI 2008), so the mortality inflicted by the lumpsucker fishery on the harbour seals has probably been reduced in the last decade

  • This may have led to the beginning of a recovery of the Icelandic harbour seal population, as indicated by the growth rate of 5% observed between 2003 and 2006 (Hauksson and Einarsson 2010)

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Summary

INTRODUCTION

In the 9th century, when Iceland was settled there is indication of large abundance of seals and many locations are named after seals and sealing (Kristjánsson 1980, Hallgrímsson 1985). The fishing is mainly conducted in the period from March to June in shallow waters and the fishing effort is quite variable and fluctuates inter-annually with the demand for roe on fishing markets It peaked in mid 1980’s and 1990’s but has been relatively low since 1997 (MRI 2008), so the mortality inflicted by the lumpsucker fishery on the harbour seals has probably been reduced in the last decade. This may have led to the beginning of a recovery of the Icelandic harbour seal population, as indicated by the growth rate of 5% observed between 2003 and 2006 (Hauksson and Einarsson 2010)

THROUGH HISTORY
DISTRIBUTION AND MOVEMENTS
LIFE HISTORY PARAMETERS
ROLE IN THE ECOSYSTEM
AND PARASITES
OTHER THAN HUNTING
Findings
ICELANDIC HARBOUR SEAL
Full Text
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