Size (acres) | 76,322 |
Percent Public Ownership | 41 |
Miles of anadromous salmonid streams | 108 |
Highest elevation (feet) | 4,486 |
Lowest elevation (feet) | 572 |
The Myrtle Creek fifth-field watershed is located in the south-central portion of the Umpqua Basin just east of Interstate Five. The watershed is 76,322 acres and stretches a maximum of 11 miles north to south and 17 miles east to west. Myrtle Creek is a tributary of the South Umpqua River.
Although less than one stream mile in length, Myrtle Creek is locally considered the mainstem stream in the watershed. North Myrtle Creek (18 stream miles) and South Myrtle Creek (22 stream miles) are tributaries to Myrtle Creek.
Most of the watershed is fairly steep with stream channels dissecting the landscape. The lowest point in the watershed is 572 feet where Myrtle Creek meets the South Umpqua River in the southwest, and the highest point is 4,486 feet at Deadman Mountain on the southeastern border of the Cascades. For most of the watershed, elevation ranges from 700 to 1,000 feet. North and South Myrtle creeks both have narrow floodplains, generally less than a quarter mile in width; as these streams converge to form Myrtle Creek, the floodplain valley become broader.
Approximately 83% of the City of Myrtle Creek is within the Myrtle Creek Watershed. Most of the population in the watershed lives within the City of Myrtle Creek and in the valley bottoms along North and South Myrtle creeks and their major tributaries. North Myrtle Road and South Myrtle Road provide access to the eastern portion of the watershed.
The most common land use in the Myrtle Creek Watershed is forestry, with over 79% of the land base used for public or private forestry. Agriculture constitutes 18%, and mostly occurs near the City of Myrtle Creek and within the South Myrtle Creek Valley. Land ownership is primarily private (57%), with public ownership mostly administered by the Bureau of Land Management.
In the Myrtle Creek Watershed, coho, winter steelhead, and cutthroat trout are the only salmonids with resident populations or annual runs. Although spring and fall chinook have been documented in Myrtle Creek, North Myrtle Creek, and South Myrtle Creek, their presence is intermittent and does not constitute a run. Warm water fish, including largemouth bass, smallmouth bass, yellow perch, bluegill, brown bullhead, and pumpkinseed, have also been reported in the watershed. These fish are most likely introduced to streams through private ponds, or migrate into the watershed from the South Umpqua River.
Myrtle Creek, North Myrtle Creek, South Myrtle Creek, and the lower reaches of many larger tributaries have riparian areas that are mostly thin strips of hardwoods interspersed with shrubs and blackberries. The upper reaches of North and South Myrtle creeks and their tributaries are mostly conifer forests; these areas correspond with lands used for public and private forestry. Oregon Department of Fish and Wildlife (ODFW) stream habitat surveys conducted in 1994 suggest that poor riffles and poor levels of large woody debris limit salmonid habitat in Myrtle Creek, North Myrtle Creek, South Myrtle Creek, and many of the tributaries.
In the Myrtle Creek Watershed, portions of North and South Myrtle creeks and seven of their tributaries are on the Oregon Department of Environmental Quality (ODEQ) 303(d) list for violating stream temperature standards. North and South Myrtle creeks are also considered water quality limited for flow modification, and North Myrtle Creek is water quality limited for habitat modification. In the ODEQ 303(d) list, Myrtle Creek is considered part of North Myrtle Creek and not a separate stream. Therefore, Myrtle Creek is also 303(d) listed for temperature and considered water quality limited for habitat and flow modification.
In 2002, most of Myrtle Creek was 303(d) listed for ammonia. The cause of the high ammonia values was effluent discharged from the Myrtle Creek and Tri-City wastewater treatment plant during times of low stream flow. In 2003, the wastewater treatment plant was extensively renovated and is now in compliance with ODEQ water quality standards. The Roseburg office of the ODEQ believes Myrtle Creek can be removed from the 303(d) list for ammonia toxicity.
1. Actively seek out opportunities with landowners, businesses, and resident groups in key areas to enlist participation in the following restoration projects and activities:
Big Lick Creek - monitor for fish presence.
Bilger Creek - instream enhancement (all) and riparian fencing/stock water, tree planting, and blackberry conversion (headwaters and mouth).
Buck Fork Creek - instream enhancement (all).
Cedar Hollow - monitor for fish presence.
Frozen Creek - riparian fencing/stock water, tree planting, and blackberry conversion (lower two-thirds).
Harrison Young Brook - monitor for fish presence.
Lally Creek - monitor for fish presence.
Lees Creek - instream enhancement (all).
Long Wiley Creek - monitor for fish presence (also on Short Wiley Creek).
Louis Creek - instream enhancement (upper two-thirds), riparian fencing/stock water, tree planting, and blackberry conversion (lower half). Also monitor for fish presence on upper reaches.
North Myrtle Creek - instream enhancement (upper reaches), riparian fencing/stock water, tree planting, and blackberry conversion (between Lees Creek and Buck Fork Creek and between Frozen Creek and Slide Creek).
School Hollow Creek - riparian fencing/stock water, tree planting, and blackberry conversion (all). Also monitor for fish presence.
Slide Creek - instream enhancement (all), riparian fencing/stock water, tree planting, and blackberry conversion (lower half).
South Myrtle Creek - instream enhancement (upper reaches).
Weaver Creek - instream enhancement (all).
2. Work with interested landowners on a case-by-case basis on the following project types:
3. Develop educational materials and/or outreach programs to educate target audiences about fish habitat and water quality-related issues:
4. Support local fish habitat and water quality research:
5. Enlist landowner participation to remove other fish passage barriers as identified. Work with landowners to eliminate barriers to fish passage at the following locations:
Geyer, Nancy A. Myrtle Creek Watershed Assessment and Action Plan. Roseburg, Oregon: Prepared for the Umpqua Basin Watershed Council; 2003 June.