
Life history and essential habitats of humpback whitefish in Lake Clark National Park, Kvichak River watershed, Alaska
(continued)
DISCUSSION
Although humpback whitefish are the second most important subsistence fish species harvested in the Kvichak River watershed, few data are available to assist managers in evaluating a reported recent decline in this species’ abundance. Initial research on humpback whitefish in Lake Clark National Park began in 2005, and indicates they are both attracted to and derive nutrients from anadromous sockeye salmon. We capitalized on this behavior and were able to easily sample humpback whitefish with seines and gillnets in areas baited with salmon eggs. Ice fishing was also found to be a viable, but slow capture method.
Similar to results obtained from Canadian studies of lake whitefish (Barnes and Power 1984), our age estimates of humpback whitefish were the same from both scales and otoliths for the first three years of life, after which, age estimates from these two structures began to vary. The difficultly in obtaining accurate age estimates suggests an age validation study would be useful to this and other similar studies. In Lake Clark this could be accomplished by marking and recapturing humpback whitefish of various sizes in a small system such as the Pickeral Lakes, assuming they exhibit site fidelity and that a wide range of ages could be marked.
Size distribution for the population based on samples obtained from seines, variable mesh gillnets and hook and line fishing indicate a bimodal frequency distribution. This type of distribution is similar to that observed for other whitefish species and lake trout in Arctic systems of Canada (Power 1984). Our growth equations (Figure 8) indicate rapid growth until age 4 – 7, which is likely when individuals become sexually mature which would slow growth rates. The lack of individuals of intermediate sizes could be due to differences in year class strength, selection by the subsistence fishery or predators. After fish reach a size of ≥ 380 mm, predation likely declines and mortality in the population may stabilize at a low level for the rest of the life span.
The lack of a strong Sr spike in the 10 otoliths analyzed for anadromy suggests Lake Clark whitefish either remain in freshwater throughout their life, or that they use estuarine areas with very low salinities. The high variation observed in the Sr signal of some fish may be due to spending time in a low salinity estuary, extensive vertical movements within freshwater, or feeding on anadromous sockeye salmon carcasses and eggs. Further study is needed to tease out potential causal factors. The radio telemetry work planned for 2006 may allow us to determine whether some Lake Clark whitefish are anadromous.
ACKNOWLEDGEMENTS
This project was made possible by a grant from the Federal Office of Subsistence Management, U.S. Fish and Wildlife Service, logistical support from the friendly staff at Lake Clark National Park and Preserve; Bristol Bay Native Association Interns including Tim Dyasuk and Tatiana Askoak. Theresa Rickteroff assisted with whitefish sampling and the people of Nondalton gave invaluable advice on fishing and potential capture locations.
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Appendix I. Example of the humpback whitefish ACCESS database documenting sampling locations, general habitat type and whether humpback whitefish were captured in that habitat.
| Sampling Locations Table |
ID |
Drainage |
Water Body |
Specific Location |
Latitude |
Longitude |
Habitat Type |
Humpback Whitefish? |
1 |
Lake Clark |
Sucker Bay |
North Point |
60.03452 |
-154.65990 |
Lacustrine |
Yes |
2 |
Lake Clark |
Sucker Bay |
West Shore |
60.03352 |
-154.66391 |
Lacustrine |
No |
3 |
Lake Clark |
Sucker Bay |
East Shore |
60.03424 |
-154.66122 |
Lacustrine |
No |
4 |
Sixmile Lake |
Pickeral Lakes |
Middle Pickeral Lake |
60.00228 |
-154.68863 |
Lacustrine |
Yes |
5 |
Sixmile Lake |
Pickeral Lakes |
Lower Pickeral Lake |
59.94745 |
-154.74532 |
Lacustrine |
Yes |
6 |
Sixmile Lake |
Pickeral Lakes |
Lower Lake Outlet |
59.94700 |
-154.74000 |
Riverine |
Yes |
7 |
Sixmile Lake |
Newhalen River |
East Bank |
59.94897 |
-154.85942 |
Riverine |
Yes |
8 |
Sixmile Lake |
Newhalen River |
West Bank |
59.94374 |
-154.86653 |
Riverine |
Yes |
9 |
Chulitna River |
Long Lake |
West End |
60.13332 |
-155.11555 |
Lacustrine |
Yes |
10 |
Chulitna River |
Long Lake |
East End |
60.14605 |
-155.01315 |
Lacustrine |
Yes |
11 |
Little Lake Clark |
Little Lake Clark |
Outlet of Waterfall Stream |
60.38381 |
-153.75661 |
Lacustrine |
Yes |
12 |
Little Lake Clark |
Little Lake Clark |
Outlet of Large Tributary |
60.38635 |
-153.75560 |
Lacustrine |
No |
13 |
Little Lake Clark |
Little Lake Clark |
Outlet of Small Tributary |
60.41901 |
-153.64772 |
Lacustrine |
No |
14 |
Little Lake Clark |
Little Lake Clark |
Head of Lake |
60.44230 |
-153.61101 |
Lacustrine |
No |
15 |
Lake Clark |
Chulitna Bay |
Owl Bluff Island |
60.20422 |
-154.45186 |
Lacustrine |
Yes |
16 |
Lake Clark |
Chulitna Bay |
Indian Point |
60.18213 |
-154.54840 |
Lacustrine |
Yes |
17 |
Lake Clark |
Chulitna Bay |
North Shore |
60.20245 |
-154.49315 |
Lacustrine |
No |
18 |
Lake Clark |
Chi Point |
Bill and Martha's |
60.07444 |
-154.60583 |
Lacustrine |
No |
19 |
Lake Clark |
Port Alsworth |
Hardenburg Bay |
60.20316 |
-154.30487 |
Lacustrine |
Yes |
20 |
Lake Clark |
Chulitna Bay |
Indian Point Island |
60.18042 |
-154.55276 |
Lacustrine |
Yes |
21 |
Lake Clark |
Chulitna Bay |
West End |
60.18205 |
-154.58353 |
Lacustrine |
Yes |
23 |
Chulitna River |
Chulitna River |
Lower |
60.18205 |
-154.58353 |
Riverine |
No |
24 |
Lake Clark |
Lake Clark |
Mouth of Kijik River |
60.28427 |
-154.22836 |
Lacustrine |
Yes |
25 |
Lake Clark |
Lake Clark |
Priest Rock |
60.30828 |
-154.17600 |
Lacustrine |
No |
26 |
Lake Clark |
Lake Clark |
Island near Hammond's |
60.00000 |
-154.00000 |
Lacustrine |
No |
27 |
Lake Clark |
Lake Clark |
Mouth of Portage Creek |
60.35029 |
-154.01547 |
Lacustrine |
No |
28 |
Lake Clark |
Kijik Lake |
Outlet |
60.30790 |
-154.29328 |
Riverine |
No |
|