Tainter Creek, Reads and Tainter Creeks Watershed (LW03)
Tainter Creek, Reads and Tainter Creeks Watershed (LW03)
Tainter Creek (1185500)
12.58 Miles
2.45 - 15.03
Natural Community
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.
Cool-Cold Mainstem, Cool-Cold Headwater, Coldwater
Year Last Monitored
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.
2024
Poor
 
This river is impaired
Elevated Water Temperature
Unknown Pollutant
 
Crawford, Vernon
Trout Water 
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.
Yes
Outstanding or Exceptional 
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.
Yes
Impaired Water 
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.
Yes

Fish and Aquatic Life

Current Use
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.
Restricted Aquatic Life
Fish and Aquatic Life communities are not fully supported in this ecosystem.
Attainable Use
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.
Cold (Class I Trout)
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.
Designated Use
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.
Cold
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.

Overview

Tainter Creek begins in south central Vernon and flows into north central Crawford County. This stream flows in a south easterly direction for 6.8 miles until it reaches the Kickapoo River north of Gays Mills. Tainter Creek has a rather steep gradient of 50 feet per mile through Vernon County, but a more gentle gradient of 15 feet per mile through Crawford County. This stream drains forested hillsides and agricultural valleys as well as the agricultural headwater plateau. Tainter Creek is a Class II trout stream upstream of CTH B and an exceptional water resources for 4.8 miles and Class III downstream for the remaining two miles. The most recent survey, conducted in 1985, documented a fairly substantial brown trout population. A 1974 survey documented not only brown trout, but also a very diverse forage fishery. The stream bottom consisted primarily of cobble and gravel in the upper reaches and
gradually more sand further downstream. In-stream cover included undercut banks, boulders, and woody debris. Much of Tainter Creek contains a stream channel incised into the valley floor resulting in vertical raw streambanks which consistently contribute sediment to the stream. Repairing these vertical banks would benefit the in-stream habitat of Tainter Creek. A fish and habitat survey should be conducted of Tainter Creek to determine its existing condition. Tainter Creek would benefit from the purchase of streambank easements from willing sellers and the restoration of in-stream habitat. WDNR records indicate that Tainter Creek was stocked with brown trout from 1973 to 1997. From 1998 to present both wild brook trout and wild brown trout have been stocked. Access to Tainter Creek is from six road
crossings, WDNR owned land and WDNR easements.

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

The trout fishery in Tainter Creek has good potential for improvement if nonpoint source water pollution is controlled. Livestock pasturing the streambank has degraded in-stream habitat.

Date  1994

Author   Surface Water Inventory Of Wisconsin

Historical Description

Tainter Creek, T11N, R4W, Section 18. Surface Acres = 6.1, Miles = 3.6, Gradient = 50.0 feet per mile.
A clear, hard water tributary of the Kickapoo River. It heads in Vernon County, flows in a
southerly direction, and joins the Kickapoo in Crawford County. The stream is Class II brown trout water. White sucker, Johnny darter and slimy sculpin are among the forage fish present. Scattered open water areas were observed in the lower two-thirds of the stream (in Vernon County) during the winter aerial groundwater survey. Rubble is slightly dominant over gravel, with silt, sand, hardpan, and boulder comprising the remainder of the bottom types. There is access from three road crossings. Beaver are present and muskrat are significant. There is some wood duck nesting along the stream.

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

Date  1973

Author   Surface Water Inventory Of Wisconsin

Tainter Creek, Reads and Tainter Creeks Watershed (LW03) Fish and Aquatic LifeTainter Creek, Reads and Tainter Creeks Watershed (LW03) RecreationTainter Creek, Reads and Tainter Creeks Watershed (LW03) Fish Consumption

Impaired Waters

Tainter Creek was recently evaluated during the ten-year period of 2009 through 2018 for results that were reported to the USEPA for the 2020 Clean Water Act condition report. The waterbody is considered impaired, or in poor condition for designated uses which include the quality of fish and aquatic life, recreational use, and public health and welfare (fish consumption and related). Pollutants or problems encountered during sampling (impairments) are determined based on water quality standards outlined in Wisconsin 2020 Consolidated Assessment and Listing Methodology (WisCALM). Assessment results show water conditions that are potentially harmful for Aquatic Life use due to values for temperature and macroinvertebrates that fall into the range expected for an aquatic community in poor health, therefore this water is listed as impaired.


Tainter Creek (mile 0-2.45): This portion of the creek is in excellent condition for Aquatic Life use and good condition for Fish Consumption use.

Tainter Creek (mile 2.45-15.03): Assessment results during the 2020 listing cycle show elevated water temperature levels inappropriate for Aquatic Life use according to 2020 WisCALM standards. Available bug sample data (macroinvertebrate Index of Biotic Integrity) show poor condition. Available fish data and new total phosphorus data do not indicate impairment. Based on the most updated information, this water was proposed for the impaired waters list in 2020.

Date  2019

Author  Ashley Beranek

Condition

Wisconsin has over 84,000 miles of streams, 15,000 lakes and milllions of acres of wetlands. Assessing the condition of this vast amount of water is challenging. The state's water monitoring program uses a media-based, cross-program approach to analyze water condition. An updated monitoring strategy (2015-2020) is now available. Compliance with Clean Water Act fishable, swimmable standards are located in the Executive Summary of Water Condition in 2018. See also the 'monitoring and projects' tab.

Reports

Recommendations

Citizen-Based Stream Monitoring
Collect chemical, physical, and/or biological water quality data to assess the current overall stream health. The data can inform management decisions and may be used to identify impaired waters for biennial lists.

Management Goals

Wisconsin's Water Quality Standards provide qualitative and quantitative goals for waters that are protective of Fishable, Swimmable conditions [Learn more]. Waters that do not meet water quality standards are considered impaired and restoration actions are planned and carried out until the water is once again fishable and swimmable

Management goals can include creation or implementation of a Total Maximum Daily Load analysis, a Nine Key Element Plan, or other restoration work, education and outreach and more. If specific recommendations exist for this water, they will be displayed below online.

Monitoring

Monitoring the condition of a river, stream, or lake includes gathering physical, chemical, biological, and habitat data. Comprehensive studies often gather all these parameters in great detail, while lighter assessment events will involve sampling physical, chemical and biological data such as macroinvertebrates. Aquatic macroinvertebrates and fish communities integrate watershed or catchment condition, providing great insight into overall ecosystem health. Chemical and habitat parameters tell researchers more about human induced problems including contaminated runoff, point source dischargers, or habitat issues that foster or limit the potential of aquatic communities to thrive in a given area. Wisconsin's Water Monitoring Strategy was recenty updated.

Grants and Management Projects

Monitoring Projects

Watershed Characteristics

Tainter Creek is located in the Reads and Tainter Creeks watershed which is 135.69 miĀ². Land use in the watershed is primarily forest (47.20%), agricultural (24%) and a mix of grassland (23.30%) and other uses (5.50%). This watershed has 339.00 stream miles, 221.66 lake acres and 1,867.13 wetland acres.

Nonpoint Source Characteristics

This watershed is ranked High for runoff impacts on streams, Not Ranked for runoff impacts on lakes and High for runoff impacts on groundwater and therefore has an overall rank of High. This value can be used in ranking the watershed or individual waterbodies for grant funding under state and county programs.However, all waters are affected by diffuse pollutant sources regardless of initial water quality. Applications for specific runoff projects under state or county grant programs may be pursued. For more information, go to surface water program grants.

Natural Community

Tainter Creek is considered a Cool-Cold Mainstem, Cool-Cold Headwater, Coldwater under the state's Natural Community Determinations.

Natural communities (stream and lake natural communities) represent model results and DNR staff valiation processes that confirm or update predicted conditions based on flow and temperature modeling from historic and current landscape features and related variables. Predicated flow and temperatures for waters are associated predicated fish assemblages (communities). Biologists evaluate the model results against current survey data to determine if the modeled results are corect and whether biological indicators show water quaity degradation. This analysis is a core component of the state's resource management framework. Wisconsin's Riverine Natural Communities.

Cool (Cold-Transition) Mainstem streams are moderate-to-large but still wadeable perennial streams with cold to cool summer temperatures. Coldwater fishes are common to uncommon, transitional fishes are abundant to common, and warm water fishes are uncommon to absent. Headwater species are common to absent, mainstem species are abundant to common, and river species are common to absent.

Cool (Cold-Transition) Headwaters are small, usually perennial streams with cold to cool summer temperatures. Coldwater fishes are common to uncommon (<10 per 100 m), transitional fishes are abundant to common, and warm water fishes are uncommon to absent. Headwater species are abundant to common, mainstem species are common to absent, and river species are absent.

Fisheries & Habitat

Trout Classes updated in 2008 -- David Vetrano, Cindy Koperski, October 2003, 608 785-9009, This classification is based upon a survey that indicates the upper 4.8 miles of Tainter Creek is a high quality trout stream, having sufficient natural reproduction to sustain populations of wild trout at or near carrying capacity. Brown trout natural reproduction CTH B upstream - to headwaters. (Class I)

Date  2008

Author  Cynthia Koperski

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