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Part I: Seals teeth and whales ears - Scott Polar Research Institute ...

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catching to the breeding season. Fortunately when my recommendations turned out<br />

to be succeeding, a full time sealing inspector was appointed in 1956, the additional<br />

safeguard of sample counts was introduced <strong>and</strong> marking experiments begun. Now I<br />

should go into more detail.<br />

Population Studies<br />

How did I come to conclude that a progressive decline of the stock had set in?<br />

What were the results of my preliminary assessment of the overall population <strong>and</strong> its<br />

composition <strong>and</strong> dynamics? My conclusions as to the optimum target age<br />

distribution of the catch? The application of the results of my population studies to<br />

management?<br />

Evidence of progressive deterioration up to 1952. I extracted, from the CAP records <strong>and</strong><br />

the Magistrates’ reports, details of the annual catches of seals at South Georgia over<br />

the period 1910 to 1951. (Up to 1927 some 752 leopard seals <strong>and</strong>, up to 1916, 97<br />

Weddell seals had been taken, averaging about 50 a year, but this had little effect on<br />

the results). The total number taken up to 1951 was 193,328 mainly adult male<br />

elephant seals, which produced 299,000 barrels of oil or 1.6 barrels per seal. This was<br />

several times the return from an uncontrolled slaughter of the whole herd, as had<br />

taken place in the nineteenth century. It demonstrated, if indeed that is necessary, the<br />

value of rational exploitation in producing a sustained yield. But there was evidence<br />

to suggest that from the late 1930s onwards the condition of the herd had been<br />

progressively worsening in spite of the conservation measures then in place. The<br />

first hint was given in the Magistrate’s annual report for 1936, which stated that<br />

although there was no sign of diminution of numbers, the animals were vacating the<br />

large open beaches for smaller beaches often inaccessible to sealers. The reports for<br />

1939 <strong>and</strong> 1945 also remarked on the increase in the size of the colonies on these<br />

smaller beaches, <strong>and</strong> it was evident to me in 1951 that many of the large open<br />

beaches were under-populated.<br />

As a measure of the relative size of an exploited population over time we can<br />

define a unit of fishing or hunting effort <strong>and</strong> then calculate the changes in the size of<br />

the catch per unit of effort (CPUE) which occur from year to year. This is a well<br />

known practice in fishery research where it gives a measure of the density of fish<br />

stocks in the sea. So far as I know, it had not then been deployed to study mammals<br />

In the case of the elephant seal, the most convenient unit of effort – probably the only<br />

one - was the catcher’s day’s work (CDW). This was not open to the same objection<br />

as the CDW as a unit of effort in whaling research, where the factor of gear saturation<br />

(days of ‘stop catch’) was significant. Nor had there been much change in the type of<br />

ship used or in the method of working the beaches. Reliable data for calculating<br />

CDW were available to me only from 1931 onwards (in the Magistrates’ reports) <strong>and</strong><br />

in the period 1931 to 1951 there had been no change in the ships engaged, <strong>and</strong> very<br />

little if any change in the nature of the operations. However, the spring sealing<br />

operations had shifted to a later date, so variation in the length <strong>and</strong> timing of the<br />

season could perhaps affect the figures for CPUE s calculated for the whole period of<br />

spring sealing. In order to minimise this possible source of error, effort data were<br />

calculated only for October sealing which had usually accounted for well over half of<br />

418

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