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West Babine Sustainable Resource Management Plan

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The <strong>Babine</strong> River is considered Classified Waters in order to maintain opportunities for “any<br />

class of angler to participate in a fishery in a relatively unspoiled, uncrowded environment” (BC<br />

Fisheries, 2002). The classified waters system was established to recognize high quality trout<br />

rivers in BC, in particular steelhead rivers, and to maintain angling opportunities for resident<br />

anglers in those waters. The classification prescribes the level of angling use and guiding activity<br />

and allocates use between classes of anglers (BC residents, other Canadians, non-Canadians).<br />

Class 1 rivers are premier waters where the level of guided use is restricted.<br />

Summer-run steelhead populations travel up the Skeena during the summer months and arrive in<br />

the <strong>Babine</strong> system in late summer and fall to spawn. The principle spawning ground for<br />

steelhead is outside of the plan area and runs from the counting fence to Nilkitkwa lake. The<br />

largest concentration of steelhead occurs just below the outlet of <strong>Babine</strong> Lake (GTOWPG,<br />

2002). Within the plan area, steelhead spawning has been documented in the Hanawald and<br />

Shelagyote Creeks, and in the headwaters of the Nichyeskwa Creek (Gottesfeld et al, 2002).<br />

Sports fishing also occurs on the lower Shelagyote River and on some of the lakes in the <strong>West</strong><br />

<strong>Babine</strong>. Other sport fish include Chinook, Sockeye, Coho, bull trout, Dolly Varden char, lake<br />

trout, and rainbow trout. Within the plan area, bull trout primarily occur in the Shelagyote River<br />

and its tributaries.<br />

The <strong>Babine</strong>-Nilkitkwa lake system supports the largest sockeye salmon population in Canada<br />

(GTOWPG, 2002). The <strong>Babine</strong> population has accounted for 75 – 95 per cent of the Skeena<br />

sockeye production, averaging more than 3.8 million adult fish annually since 1990 (DFO,<br />

1999). Much of this high productivity can be attributed to artificial channels in the Fulton River<br />

and Pinkut Creek, outside of the plan area, which typically account for more than 70 per cent of<br />

smolt production from the <strong>Babine</strong>-Nilkitkwa lake system.<br />

The <strong>Babine</strong> chinook are one of the most important of the Skeena chinook populations<br />

(GTOWPG, 2002). The <strong>West</strong> <strong>Babine</strong> provides rearing and migration habitat for most of the<br />

Chinook populations in the <strong>Babine</strong> drainage, with documented spawning runs on the Shelagyote<br />

River and Nichyeskwa Creek (DeGisi, 2000 as cited in GTOWPG, 2002). Pink runs represent<br />

approximately 4% of the total Skeena watershed escapement (Gottesfeld et al. 2002) and Chum<br />

are present but are not abundant. <strong>Babine</strong> coho stocks are currently depressed in abundance and of<br />

high conservation concern (GTOWPG, 2002). Coho do not spawn in the plan area.<br />

The <strong>Babine</strong> fishery is of very high importance to the Gitxsan and Lake <strong>Babine</strong> Nation.<br />

Traditionally, the fishery provided food, trade goods, as well as cultural expression and<br />

connection to ancestral practices (GTOWPG, 2002). The Gitxsan salmon fishery at Kisgegas<br />

Canyon is thought to have been the largest traditional aboriginal fishery in the Skeena watershed<br />

(GTOWPG, 2002), while the major Lake <strong>Babine</strong> Nation fishery occurred outside of the plan<br />

area, around Nilkitkwa Lake.<br />

Fishing continues to be an integral cultural practice and sustenance activity for the Gitxsan and<br />

Lake <strong>Babine</strong> Nation. Salmon is a fundamental food source and the sockeye run is, and has been,<br />

particularly important to the First Nations. Fort <strong>Babine</strong> Enterprises operates an Excess Salmon to<br />

Spawning Requirement (ESSR) fishery targeting sockeye jacks harvested from the <strong>Babine</strong> at the<br />

counting fence outside of the plan area, primarily by dip-netting (Gottesfeld et al, 2002). In<br />

March 2004 Page 55

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