Elk Creek, Middle Kickapoo River Watershed (LW05)
Elk Creek, Middle Kickapoo River Watershed (LW05)
Elk Creek (1191700)
4.29 Miles
1.91 - 6.20
Macroinvertebrate, Cool-Cold Headwater, Coldwater
2016
Good
 

Overview

Elk Creek, located in central Vernon County and northwest Richland County, flows in a
northwesterly direction for 4.4 miles before reaching the Kickapoo River between Viola and
Readstown. This stream has a gradient of 46 feet per mile and drains forested hillsides and
agricultural valleys. Elk Creek is a Class I trout stream for its entire length in both Richland
(2.8 miles) and Vernon (1.6 miles) Counties. The Richland County portion of Elk Creek is
also designated as an Outstanding Resource Water (ORW).
The most recent biological surveys, conducted in 1987 and 1990, documented brown trout,
rainbow trout, brook trout and numerous forage fish species. The stream bottom was
dominated by gravel and sand. In-stream cover consisted of boulders, overhanging grasses
and aquatic vegetation. Streambank grazing of livestock was contributing sediment to the
stream. Elk Creek should be resurveyed after conclusion of the Middle Kickapoo River
Priority Watershed Project in 2004. This stream would benefit from the purchase of
streambank easements from willing sellers and the restoration of in-stream habitat.
Maintenance of WDNR owned lands adjacent to Elk Creek must include tree and brush
removal from streambanks to reduce beaver colonization. WDNR records indicate that Elk
Creek was stocked regularly with brown trout until 1988. Access to Elk Creek is from three
road crossings and WDNR owned land.

From: Ripp, Coreen, Koperski, Cindy and Folstad, Jason. 2002. The State of the Lower Wisconsin River Basin.
PUBL WT-559-2002. Wisconsin Department of Natural Resources, Madison, WI.

Date  2002

Author  Cynthia Koperski

Historical Description

Elk Creek. T12~1. R3W. Section 35. Surface Acres = 3.0. Miles =.6. Gradient = 20.0 feet per mile
A clear. hard water stream that heads in Richland County. flows in a general northwesterly direction. and is a tributary of the Kickapoo River. That portion of the stream in Vernon County is Class III brown trout water. The winter aerial groundwater survey for Vernon County found scattered open water areas in the lower two-thirds of the stream. Gravel is the dominant bottom type. with considerable sand and rubble as well as some silt, clay, and boulders. Access is possible from two road crossings. Beaver are present.

From: Klick, Thomas A. and Threinen, C.W. 1973. Lake and Stream Classification Project. Surface Water Resources of Vernon County, Wisconsin Department of Natural Resources, Madison, WI.

Date  1973

Author   Surface Water Inventory Of Wisconsin

Natural communities (stream and lake natural communities) represent model results that use predicted flow and temperature based on landscape features and related assumptions. Ranges of flow and temperature associated with specific aquatic life communities (fish, macroinvertebrates) help biologists identify appropriate resource management goals. Wisconsin Natural Communities.
This is the most recent date of monitoring data stored in SWIMS. Additional surveys for fish and habitat may be available subsequent to this date.
Trout Waters are represented by Class I, Class II or Class III waters. These classes have specific ecological characteristics and management actions associated with them. For more information regarding Trout Classifications, see the Fisheries Trout Class Webpages.
Wisconsin has designated many of the state's highest quality waters as Outstanding Resource Waters (ORWs) or Exceptional Resource Waters (ERWs). Waters designated as ORW or ERW are surface waters which provide outstanding recreational opportunities, support valuable fisheries and wildlife habitat, have good water quality, and are not significantly impacted by human activities. ORW and ERW status identifies waters that the State of Wisconsin has determined warrant additional protection from the effects of pollution. These designations are intended to meet federal Clean Water Act obligations requiring Wisconsin to adopt an 'antidegradation' policy that is designed to prevent any lowering of water quality - especially in those waters having significant ecological or cultural value.
A water is polluted or 'impaired' if it does not support full use by humans, wildlife, fish and other aquatic life and it is shown that one or more of the pollutant criteria are not met.
The use the water currently supports. This is not a designation or classification; it is based on the current condition of the water. Information in this column is not designed for, and should not be used for, regulatory purposes.
Waters that support fish and aquatic life communities (healthy biological communities).
The use that the investigator believes the water could achieve through managing "controllable" sources. Beaver dams, hydroelectric dams, low gradient streams, and naturally occurring low flows are generally not considered controllable. The attainable use may be the same as the current use or it may be higher.
Streams supporting a cold water sport fishery, or serving as a spawning area for salmonids and other cold water fish species through natural reproduction. Representative aquatic life communities, associated with these waters, generally require cold temperatures and concentrations of dissolved oxygen that remain above 6 mg/L. Since these waters are capable of supporting natural reproduction, a minimum dissolved oxygen concentration of 7 mg/L is required during times of active spawning and support of early life stages of newly-hatched fish.
This is the water classification legally recognized by NR102 and NR104, Wis. Adm. Code. The classification determines water quality criteria and effluent limits. Waters obtain designated uses through classification procedures.
Streams capable of supporting a cold water sport fishery, or serving as a spawning area for salmonids and other cold water fish species. Representative aquatic life communities, associated with these waters, generally require cold temperatures and concentrations of dissolved oxygen that remain above 6 mg/L. Since these waters are capable of supporting natural reproduction, a minimum dissolved oxygen concentration of 7 mg/L is required during times of active spawning and support of early life stages of newly-hatched fish.