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

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with the exception of division II, many of the large beaches still held very sizeable<br />

colonies in 1951.<br />

Other evidence supported this. The average harem size at the Dartmouth Point<br />

reserve in 1951, where sealing was prohibited, was 1 male to 24 cows <strong>and</strong> the overall<br />

mature sex ratio there 1:13. In contrast, at Hestesletten <strong>and</strong> Maiviken, Cumberl<strong>and</strong><br />

Bay, exploited beaches, the average harem sizes were 46 <strong>and</strong> 52 respectively <strong>and</strong> the<br />

mature sex ratios were respectively 1:28 <strong>and</strong> 1:34 – although seals had not been<br />

removed from these beaches thus far that season. The interpretation of the figures<br />

was complicated by the fact that sealing operations were continually removing a<br />

proportion of males from these exploited beaches, replaced by other males, fresh<br />

from the sea. [Also the average age of the bulls was much lower than expected in an<br />

unexploited herd, including sexually mature animals only [41/2] yrs old. In some<br />

areas it was very much below the usual age at which harems are acquired in an<br />

unexploited herd.<br />

I made an estimate of the size of the stock in the various divisions. In November<br />

1951 I counted all the pups on the beaches visited in areas I <strong>and</strong> II. They leave the<br />

beaches when they are [a few] [about six] weeks old <strong>and</strong> the figures were adjusted to<br />

allow for this; regular control counts were made on Cumberl<strong>and</strong> Bay beaches. On the<br />

beaches visited in divisions I <strong>and</strong> II the proportions of cows <strong>and</strong> pups on a given date<br />

approximated to the proportions of the control counts. It was therefore assumed that<br />

divisions I, II <strong>and</strong> III (Cumberl<strong>and</strong> Bay) were more or less synchronous as regards<br />

the pupping season. The actual counts were therefore corrected (to allow for pups<br />

which had departed), by reference to the control counts.<br />

The corrected total was 31,075 <strong>and</strong> a further allowance was made for the few<br />

beaches not visited, which brought the total to about 35,000 for these two divisions. I<br />

concluded that about 20,000 of these pups were born in division I, <strong>and</strong> 15,000 in<br />

division II. Because of my previous experience the basic counts were unlikely to be<br />

much in error, though the totals were extrapolations. This could not be said for the<br />

estimates on the other two divisions, which weren’t based on counts. After talks with<br />

the sealers, in which their opinions of the relative status of the herds in divisions III<br />

<strong>and</strong> IV was sought, an arbitrary figure of 32,500 live pups was assumed for each of<br />

these divisions, making a gr<strong>and</strong> total of approximately 100,000 pups which survived<br />

to weaning. This was a very round figure, but the best I could do, given my<br />

resources! Pup mortality from birth to weaning was assessed at 2% (from more<br />

detailed observations). This gave a total estimated annual recruitment to the<br />

population of about 102,000 pups. Of these I estimated that 20% were in division I,<br />

15% in division II, <strong>and</strong> 32.5% in each of divisions III <strong>and</strong> IV. Although these<br />

estimates could only be approximate figures they were the first ever to be made <strong>and</strong><br />

served as a basis for further calculations.<br />

Other parameters used in assessing the size of the population included: the sex<br />

ratio at birth (estimated from detailed sexed samples); average ages of the sexes at<br />

sexual maturity (estimated from tooth-aged samples); the pregnancy rate of mature<br />

females, from post-mortems; information on longevity of females (from the tooth<br />

collections). Also data on the size of the commercial catches in previous y<strong>ears</strong>, <strong>and</strong> on<br />

the age composition of the commercial kill of males in 1951, were available. For the<br />

purpose of the calculations it was assumed that recruitment <strong>and</strong> natural mortality<br />

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