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Distribution, abundance and biology of Group V humpback whales ...

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Variations in the <strong>abundance</strong> <strong>of</strong> prey on feeding grounds<br />

may be directly related to the year-to-year variation in<br />

reproductive rates (Clapham 1996) <strong>and</strong> <strong>abundance</strong> on the<br />

wintering grounds (Chaloupka <strong>and</strong> Osmond 1999). Wiley<br />

<strong>and</strong> Clapham (1993) tested the hypothesis <strong>of</strong> whether or<br />

not maternal condition affects the sex ratio <strong>of</strong> <strong>of</strong>fspring.<br />

Their investigation concluded that the sex ratio <strong>of</strong> calves<br />

born to females in “superior” condition, or that had a calving<br />

interval <strong>of</strong> three years, was biased toward sons.<br />

7.4 Male reproduction <strong>and</strong> behaviour<br />

Mature male <strong>humpback</strong> <strong>whales</strong> depart the feeding grounds<br />

with mature females (Dawbin 1966). Humpback whale<br />

courting behaviour includes elaborate songs sung by males<br />

during their migration to (Charif et al.2001) <strong>and</strong> on wintering<br />

grounds (Helweg et al.1998b). Helweg <strong>and</strong> Herman (1994)<br />

found there was no difference between singing behaviour<br />

during day <strong>and</strong> night in deep water, although Au et al.(2000)<br />

found that in shallow water <strong>of</strong>f Maui there was a change in<br />

the occurrence <strong>of</strong> singing behaviour with time <strong>of</strong> day,<br />

with a peak at night.<br />

The song patterns produced by singing <strong>humpback</strong> <strong>whales</strong><br />

depend on where individuals live, with populations inhabiting<br />

different ocean basins normally singing quite distinct songs<br />

(Noad et al.2000). Singing <strong>whales</strong> have been used to<br />

determine migratory routes (Charif et al.2001), demonstrate<br />

interchange between populations (Helweg et al.1998)<br />

<strong>and</strong> as an index <strong>of</strong> <strong>abundance</strong> (Noad 1998). Mobley et<br />

al.(1988) played a variety <strong>of</strong> sounds to <strong>humpback</strong> <strong>whales</strong><br />

on wintering grounds <strong>and</strong> concluded that the different rates<br />

<strong>of</strong> behavioural response were attributed to the behaviour<br />

<strong>of</strong> sexually active males seeking to affi liate with sexually<br />

mature females.<br />

A study conducted by Frankel et al.(1995) supported<br />

the hypothesis that song functions to maintain distance<br />

between singers <strong>and</strong> McCauley et al.(1995) give a succinct<br />

description <strong>of</strong> the song <strong>and</strong> hearing capabilities<br />

<strong>of</strong> <strong>humpback</strong>s.<br />

Richardson et al.(1995) is a comprehensive review <strong>of</strong><br />

acoustics <strong>and</strong> how they relate to marine mammals. The<br />

information presented includes specifi c references to<br />

<strong>humpback</strong> <strong>whales</strong>. They concluded there is no research<br />

to demonstrate that acoustics adversely affects <strong>humpback</strong><br />

<strong>whales</strong>. However, more recent research demonstrates<br />

that <strong>humpback</strong>s alter their behaviour in response to<br />

anthropogenic noise (Miller et al.2000). Williams et al.(2002)<br />

concluded that weakening or not enforcing the minimum<br />

approach distances for the whale watching <strong>of</strong> orcas in<br />

Canada would result in higher levels <strong>of</strong> disturbance.<br />

Corkeron (1995) demonstrated that <strong>humpback</strong>s in Hervey<br />

Bay altered their behaviour when vessels were within 300m.<br />

This <strong>and</strong> several other studies show that the behaviour<br />

<strong>of</strong> <strong>humpback</strong>s is altered by the presence <strong>of</strong> vessels but it<br />

remains uncertain if the effect is detrimental (Bauer <strong>and</strong><br />

Herman 1986; Baker <strong>and</strong> Herman 1989; Bryden et al.1988).<br />

8 Population estimates <strong>and</strong> rates<br />

<strong>of</strong> increase<br />

Reviews <strong>of</strong> international data indicate a strong recovery<br />

in most studied <strong>humpback</strong> whale populations (Best 1993<br />

<strong>and</strong> Clapham 1999b). Paterson et al.(1994) suggests that<br />

the level <strong>of</strong> recovery <strong>of</strong> the <strong>Group</strong> V population, in the<br />

post-whaling period, is due to the stock experiencing no<br />

detrimental environmental factors.<br />

8.1 Southern hemisphere population<br />

estimates<br />

During 1933–1939, the estimated total number <strong>of</strong><br />

southern hemisphere baleen numbered 220,000–340,000.<br />

Approximately 10 percent <strong>of</strong> the southern hemisphere<br />

stock <strong>of</strong> baleen <strong>whales</strong> was <strong>humpback</strong> <strong>whales</strong>, <strong>and</strong> the<br />

ratio between the groups I–V was considered to be<br />

1:1:2:3:3 respectively (Matthews 1957 cited Chittleborough<br />

1965). Based on these estimates the <strong>Group</strong> V population<br />

could be estimated at 22,000–34,000 individuals for<br />

1933–1939 (Figure 8).<br />

8.2 <strong>Group</strong> V population estimates<br />

Figure 8 is a summary <strong>of</strong> the population estimates <strong>and</strong><br />

illegal catches by the Soviet fl eet for <strong>Group</strong> V <strong>humpback</strong>s<br />

during 1930–2005. Chittleborough (1965) estimates the<br />

<strong>Group</strong> V pre-whaling population numbered approximately<br />

10,000 individuals. By 1960, he estimated a population size<br />

<strong>of</strong> only 500 individuals. In 1963, the International Whaling<br />

Commission (IWC) imposed a ban on whaling, <strong>and</strong> in<br />

1964 the <strong>Group</strong> V population was estimated at just 400<br />

individuals. Until 1963, <strong>humpback</strong> population estimates<br />

were derived by modelling the fi sheries-based catch per<br />

unit effort data (Chittleborough 1965).<br />

Chittleborough (1965) compared population estimates<br />

derived by two methods <strong>and</strong> argues that for the estimate<br />

to be correct using the DeLury method, a further 5000<br />

<strong>humpback</strong>s would have had to been fi shed during the years<br />

1960 <strong>and</strong> 1961. Only 302 <strong>and</strong> 270 <strong>whales</strong> were reported<br />

to the IWC for each <strong>of</strong> those years. Although there is some<br />

uncertainty in these estimates, it is clear that during the late<br />

1950s <strong>and</strong> early 1960s, the <strong>Group</strong> V population experienced<br />

a signifi cant decline in numbers.<br />

Recent data presented by Mikhalev (2000) supports<br />

DeLury’s population estimate discussed by Chittleborough<br />

(1965). Mikhalev (2000) presented data collected by two<br />

Soviet vessels illegally whaling during the summer season<br />

<strong>of</strong> 1959 in the Antarctic Area V. The Russian vessels<br />

signifi cantly exceeded the quota for all countries by illegally<br />

fi shing a total <strong>of</strong> 11,605 individuals from the <strong>Group</strong> V<br />

population.<br />

Chittleborough (1965) estimated that the <strong>Group</strong> V population<br />

would take 36–63 years to regain its unfi shed status <strong>of</strong><br />

10,000 individuals. However in 1998, 33 years later, the<br />

<strong>Group</strong> V population was estimated at 4000 individuals<br />

(Paterson cited QDEH 1999). If a constant rate <strong>of</strong> increase<br />

is assumed, the 1962 population estimate <strong>of</strong> 500 individuals<br />

would have to have increased at a rate <strong>of</strong> approximately<br />

8 percent a year to reach its unfi shed state in 36 years.<br />

The rate <strong>of</strong> increase for the population to reach its unfi shed<br />

state in 63 years is just 4·8 percent a year. However,<br />

Mikhalev (2000) details the large-scale illegal Soviet catch<br />

data for the late 1960s <strong>and</strong> illustrates that the catches <strong>of</strong><br />

<strong>humpback</strong> on their feeding grounds during 1963–1968<br />

exceeds the population estimates derived by Chittleborough<br />

(1965). The population estimates for this period are being<br />

revised to account for the illegal catches by the Soviet fl eet<br />

(pers. comm. P Corkeron 2002).<br />

14 • <strong>Distribution</strong>, <strong>abundance</strong> <strong>and</strong> <strong>biology</strong> <strong>of</strong> <strong>Group</strong> V <strong>humpback</strong> <strong>whales</strong> Megaptera novaeangliae: A review • August 2002

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