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A Population Assessment of Lake Sturgeon in the Namakan River ...

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DISCUSSION<br />

The lake sturgeon population sampled <strong>in</strong> <strong>the</strong> <strong>Namakan</strong> <strong>River</strong> upstream <strong>of</strong> Lady Rapids<br />

appears to be healthy <strong>in</strong> both abundance and population structure, and has achieved short<br />

term goals established by <strong>the</strong> Border Waters <strong>Lake</strong> <strong>Sturgeon</strong> Management Committee<br />

(OMNR and MDNR, 1995; OMNR and MDNR, 2004; Stewig, 2005) (Appendix II).<br />

However, <strong>the</strong> limited availability <strong>of</strong> population diagnostics and biological <strong>in</strong>dicators for<br />

this species makes <strong>in</strong>terpretation <strong>of</strong> population status difficult. The sampled population<br />

<strong>in</strong> 2006-2008 conta<strong>in</strong>ed predom<strong>in</strong>antly young fish with very few older fish (> 50 years)<br />

present. Annual recruitment appears to have been consistent over <strong>the</strong> 34 year period<br />

from 1963 to 1995, based on fish that were fully recruited to <strong>the</strong> sampl<strong>in</strong>g gear and <strong>the</strong><br />

selected mesh sizes. This observation is consistent with recent population assessments on<br />

<strong>the</strong> Ra<strong>in</strong>y <strong>River</strong>/<strong>Lake</strong> <strong>of</strong> <strong>the</strong> Woods (Stewig, 2005) and on Ra<strong>in</strong>y <strong>Lake</strong> (Adams et al.,<br />

2006).<br />

Fur<strong>the</strong>r comparison <strong>of</strong> biological parameters (age, size, growth and mortality) to adjacent<br />

populations <strong>in</strong> <strong>the</strong> Ra<strong>in</strong>y <strong>River</strong>/<strong>Lake</strong> <strong>of</strong> <strong>the</strong> Woods dra<strong>in</strong>age bas<strong>in</strong> (DU6) reflects those <strong>of</strong><br />

recover<strong>in</strong>g populations. <strong>Lake</strong> sturgeon populations are reported to be recover<strong>in</strong>g <strong>in</strong> <strong>the</strong><br />

Se<strong>in</strong>e <strong>River</strong> (McLeod, 1999), Ra<strong>in</strong>y <strong>Lake</strong> (Adams et al., 2005) and Ra<strong>in</strong>y <strong>River</strong>/lake <strong>of</strong><br />

<strong>the</strong> Woods (Stewig, 2005). <strong>Population</strong>s <strong>in</strong> <strong>the</strong>se border waters collapsed <strong>in</strong> <strong>the</strong> early<br />

1900’s, primarily due to commercial over-fish<strong>in</strong>g (OMNR and MDNR, 2004). Although<br />

commercial harvest records are not available prior to 1924, exploitation was likely a<br />

factor <strong>in</strong> <strong>the</strong> current status <strong>of</strong> lake sturgeon <strong>in</strong> <strong>the</strong> <strong>Namakan</strong> Reservoir and upstream <strong>in</strong><br />

Lac La Croix. Water control dams were also constructed at <strong>the</strong> outlet <strong>of</strong> <strong>Namakan</strong><br />

Reservoir <strong>in</strong> 1914 and may have affected sturgeon migration and spawn<strong>in</strong>g conditions<br />

28

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