Spring Creek, Badfish Creek Watershed (LR07)
Spring Creek, Badfish Creek Watershed (LR07)
Spring Creek (799900)
3.43 Miles
0 - 3.43
Cool-Cold Headwater, Coldwater
2024
Fair
 

Overview

Rock River Water Quality Management Plan, Lower Rock River Appendix. WT-668-2002. South Central Region, WDNR.

Spring Creek is a small spring-fed tributary of medium grade (16 feet/mile) that connects with Badfish Creek near Cooksville. Historically, Spring Creek was managed for trout, but ditching and polluted runoff reduced it by the mid-1980s to supporting a warm water forage fishery. In 1990, Spring Creek reappeared as a trout water in the “Trout Fishing Regulations and Guide.”

As of 1996, Spring Creek is considered a Class III Trout Stream supporting brown trout; the stream's potential, however, is Class II. The effects of stream channelization and polluted runoff in the stream's six-square-mile agricultural watershed--particularly from streambank pasturing (erosion) and barnyard runoff--have taken their toll. Runoff from up-slope cultivated fields represents 95 percent of the total sediment load to streams in the watershed, which is 86 percent agricultural with row cropping the primary enterprise (83 percent of total acres). Up-slope runoff also contributes nitrate to groundwater (WDNR, 1993a).

Spring Creek was selected as a nonpoint source priority watershed project and a water resources appraisal was prepared in 1993 (WDNR, 1993b). For purposes of analysis, the stream is divided into two segments: from its headwaters to Murray Road is segment 1; east of Murray Road is considered segment 2. Segment 1 has been extensively channelized and thus exhibits habitat loss; by the mid-1950s the stream no longer supported trout. Recent land use changes have restored a buffer strip along this segment's streambanks, allowing development of riparian habitat and ecological recovery. Heavy sediment persists, however, on the stream bottom, which has accumulated during previous years' runoff and low flow conditions (WDNR, 1993b).

Segment 2 has retained its natural stream hydrology, but heavy pasturing and streambank erosion stifle the stream's functional values. Eroded streams and embeddedness reduce suitable habitat for insects and spawning fish (WDNR, 1993a). Streambanks contribute the remaining 5 percent of the overall sediment delivered to the watershed. The priority watershed plan's target goal is to reduce by 75 percent the total tons delivered from streambanks annually and restore 50 percent of the riparian habitat.

In addition, high bacteria and nutrient loads persist from poor feedlot and manure management practices. An 85 percent reduction in animal feedlot runoff from throughout the watershed is necessary to meet the priority watershed plan's stated objectives (WDNR, 1993a).

Date  2002

Author   Aquatic Biologist

Historical Description

Bush, D.M., R. Cornelius, D. Engle, and C.L. Brynildson. 1980. Lake and Stream Classification Project. Surface Water Resources of Green County, 2nd Edition. Wisconsin Department of Natural Resources, Madison, Wisconsin.

Originating near the Illinois-Wisconsin border. this warm water creek is joined by one unnamed stream and flows northwest to enter Honey Creek. Spring Creek runs through cropland and pasture and bank erosion is moderate to heavy in the pastured areas. The stream is wide and shallow and the water generally runs turbid. The bottom is approximately 60 percent gravel and 40 percent silt and muck.
The Spring Creek fishery consists of forage species dominated by the central stoneroller. Wildlife values are limited to a few muskrats and public access is available from two county road crossings.
Fish Species: .Central stoneroller, stoneroller x southern redbe)ly dace hybrid, brassy minnow, common shiner
x southern redbelly dace hybrid, bigmouth shiner, southern redbelly dace, bluntnose minnow, fathead minnow, creek chub, white sucker, brook stickleback, Johnny darter.
Surface Acres = 3.3. Length = 3.4 Miles. Gradient = 28 ft./mi.. Base Discharge = 4.3 cu ft./sec.

Date  1980

Author   Surface Water Inventory Of Wisconsin

Historical Description

From: Ball, Joseph R., and Ronald J. Poff, Lake and Stream Classification Project. Surface Water Resources of Rock County, Department of Natural Resources, 1970.

Surface Acres = 1.3, Miles = 2.75, Gradient = 16 feet per mile.

A small spring fed stream originating northeast of Evansville and flowing in a northeasterly direction to Badfish Creek. Once managed for trout but now supports only forage species. Ditching in the upper portion of the stream was partly responsible for increased water temperatures and habitat deterioration. Adjoining fresh meadow wetland totals 430 acres but has little waterfowl or marsh furbearer value. Access is available from one town road and two state highway crossings.

Date  1970

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. Representative aquatic life communities, associated with these waters, generally require cold temperatures and concentrations of dissolved oxygen that remain above 6 mg/L through natural reproduction and selective propagation. 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.