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the cougar in the santa ana mountain range, california

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may be typical of, or only moderately less than,<br />

truit of o<strong>the</strong>r populations. Three of <strong>the</strong> 4<br />

previously published rates provided<br />

unrealistically high estimates of true survival<br />

rates. Compar<strong>in</strong>g mean litter sizes near birth<br />

and at 12 months (not <strong>the</strong> same litters followed<br />

through time) Ashman et al. (1983), suggested<br />

a value of78%. Similar data <strong>in</strong> Rob<strong>in</strong>ette et al.<br />

(1961 :213, <strong>in</strong>ferr<strong>in</strong>g age from weight)<br />

suggested a survival rate of about 73%.<br />

However this method considers only litters <strong>in</strong><br />

which at least I cub survived to 12 months of<br />

age. Whenever all cubs <strong>in</strong> a litter died with<strong>in</strong><br />

12 months, <strong>the</strong> method would not detect a litter,<br />

thus ignor<strong>in</strong>g a large number of cub deaths<br />

(Rob<strong>in</strong>ette et al 1961:213). Hemker et al.<br />

(1986) followed marked animals over time,<br />

report<strong>in</strong>g a survival rate of 72% for cubs<br />

between 3 and 10 months of age and 92% for<br />

cubs from 10 months to dispersal at 16-19<br />

months, <strong>in</strong> an area of extremely low <strong>cougar</strong><br />

density (gross density of 0.5 <strong>cougar</strong>s per 100<br />

km 2 ). Hemker et al. (1986:330) cautioned that<br />

<strong>the</strong>ir estimates did not reflect overall juvenile<br />

survivorship because <strong>the</strong>y excluded <strong>the</strong> 2<br />

periods of highest mortality, namely <strong>the</strong> early<br />

neonatal period (age 0-3 months) and <strong>the</strong> postdispersal<br />

period. Their estimates also may<br />

reflect density-dependent enhancement of<br />

survival rates at low density. Us<strong>in</strong>g methods<br />

similar to ours, Anderson et al. (1992)<br />

computed <strong>the</strong> survival rate for yearl<strong>in</strong>g <strong>cougar</strong>s<br />

as 0.642, an estimate much closer to ours than<br />

<strong>the</strong> previous reports; <strong>the</strong>y did not attempt to<br />

monitor or estimate density for juveniles less<br />

than 1 year old.<br />

, In many cases, we could <strong>in</strong>fer cause of<br />

death ofjuveniles (Table 4). Vehicle accidents<br />

and be<strong>in</strong>g orphaned were <strong>the</strong> lead<strong>in</strong>g causes of<br />

death for juvenile <strong>cougar</strong>s (5 cases each).<br />

Cougar-<strong>in</strong>flicted <strong>in</strong>juries were implicated <strong>in</strong> 3<br />

deaths. These cases are discussed <strong>in</strong> greater<br />

detail <strong>in</strong> later sections of this chapter. In most<br />

o<strong>the</strong>r cases, <strong>the</strong> cause of death could not be<br />

determ<strong>in</strong>ed.<br />

42<br />

Adult survivorship<br />

Adult survivorship was computed from<br />

data on 20 adults monitored for periods oftime<br />

vary<strong>in</strong>g from 2 to 58 months, or a total of 497<br />

<strong>cougar</strong>-months. There were <strong>in</strong>sufficient data to<br />

compute survival rates separately for males and<br />

. females, and our sample was mostly females.<br />

We <strong>ana</strong>lyzed <strong>the</strong>se data us<strong>in</strong>g I-month time<br />

<strong>in</strong>tervals and <strong>the</strong> product limit procedure with<br />

staggered entry (Pollock et al. 1989). The<br />

product of 12 monthly rates yielded an estimate<br />

ofannual survival rate, and <strong>the</strong> average of<strong>the</strong>se<br />

runn<strong>in</strong>g products yielded a s<strong>in</strong>gle po<strong>in</strong>t<br />

estimate.<br />

The annual survival rate for adults was<br />

75%. This means that on average an adult had<br />

a 75% chance of be<strong>in</strong>g alive <strong>in</strong> 12 months. F7<br />

and FlO were dropped from <strong>the</strong> computations<br />

<strong>in</strong> <strong>the</strong> month we lost <strong>the</strong>ir signal. If <strong>the</strong>se<br />

animals <strong>in</strong> fact died at <strong>the</strong> time of<br />

disappearance (which is probably true for FlO<br />

at least), <strong>the</strong>n <strong>the</strong> adult survival rate was 72%.<br />

As with juveniles, vehicle accidents were <strong>the</strong><br />

lead<strong>in</strong>g cause of death (Table 5), kill<strong>in</strong>g 5<br />

adults (F8, F9, FI2, F13, FI5). Two adult<br />

<strong>cougar</strong>s (Fl, F6) were killed by o<strong>the</strong>r <strong>cougar</strong>s.<br />

Two (F2, F3) died of <strong>in</strong>test<strong>in</strong>al illnesses<br />

(probably not <strong>the</strong> same disease). Three adults<br />

(M1, M2, F II) were shot on depredation<br />

permits after eat<strong>in</strong>g goats or sheep. Two<br />

<strong>cougar</strong>s (F7, FlO) disappeared abruptly; <strong>the</strong>re<br />

is some evidence that FlO may have been<br />

poached. Each cause of death is considered <strong>in</strong><br />

greater detail <strong>in</strong> <strong>the</strong> follow<strong>in</strong>g sections.<br />

Our estimated adult survival rate of<br />

75% is higher than <strong>the</strong> approximately 68%<br />

<strong>in</strong>ferred from hunt<strong>in</strong>g returns of marked<br />

animals by Ashman et al. (1983) and from<br />

exist<strong>in</strong>g age structure by Rob<strong>in</strong>ette et al.<br />

1977: 123). Our estimate is nearly identical to<br />

<strong>the</strong> 74% observed <strong>in</strong> Utah by L<strong>in</strong>dzey et al.<br />

(1988), and somewhat lower than <strong>the</strong><br />

approximately 80-92% observed <strong>in</strong> Colorado

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