Tainter Lake, Pine Creek and Red Cedar River,Wilson Creek Watershed (LC04)
Tainter Lake, Pine Creek and Red Cedar River,Wilson Creek Watershed (LC04)
Tainter Lake (2068000)
1387.21 Acres
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.
Reservoir
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 impoundment is impaired
Excess Algal Growth, Elevated pH , Eutrophication
Mercury, Total Phosphorus
 
Dunn
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.
No
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.
No
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.
WWSF
Streams capable of supporting a warm waterdependent sport fishery. Representative aquatic life communities associated with these waters generally require cool or warm temperatures and concentrations of dissolved oxygen that do not drop below 5 mg/L.
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 Lake is a hypereutrophlc impoundment on the Red Cedar River at Cedar Falls. A water quality assessment conducted on Tainter Lake from February, 1989, through October, 1990 had as its objective determining the impacts of the annual phosphorus load on water quality in Tainter Lake and what phosphorus load reductions would significantly improve water quality (Mechelke).

The study found that growing season (May-September) phosphorus inputs had the most significant effect on water quality in Tainter Lake. The study concluded that 84 percent of these phosphorus loads are controllable, of which 9 percent can be attributed to point sources and 75 percent to polluted runoff. The study concluded that Tainter Lake water quality will not respond to small decreases in phosphorus loading. To achieve a significant reduction in chlorophyll a, representing algal populations, it would require a 65-70 percent reduction in the amount of growing season polluted runoff and phosphorus limits on point source dischargers. A recent calibration of the
model predicted that a 50-60 percent phosphorus load reduction would effect the same change (Schreiber 1995).

The water quality study concluded that it will take an intensive effort to reduce phosphorus loading throughout the Red Cedar drainage basin above Tainter Lake if water quality is to significantly improve (Schreiber). Efforts to improve other lake attributes should not be ignored. Shoreline
aesthetics and fishery habitat are two areas that could be worked on by the lake community to improve the recreational use of Tainter Lake.

Recommendations from the study include developing another study to determine the feasibility of and means of reducing the phosphorus load to Tainter Lake; establishment of long-term phosphorus monitoring stations to assess annual variability in phosphorus loads. Mercury concentrations in walleye exceed the advisory criteria in Tainter Lake, although Lake
Menomin walleye do not. The mercury concentration trend in fish is inconsistent with that seen statewide. A small sample size may be influencing the data or there may be something unique occurring in ths system. Collection of additional walleye and smallmouth bass from Tainter Lake
may help clarify the data. PCB analysis needs to be conducted on whte sucker and larger walleye and bass (Amrhein)

Date  1996

Author   Aquatic Biologist

Historical Description

A hardwater, drainage impoundment on the Red Cedar River. Hay River, Lambs Creek and another feeder stream in Section 30 also flow into Tainter Lake. All the named streams are navigable at their outlets. A 52-foot head public utility dam (Northern States Power Company) is located on the outlet (1, 200 cfs) of the lake at Cedar Falls. Managed for walleyes, bass and pan fish, its most common fish species are walleyes, perch, brown and yellow bullheads, carp and white suckers. Other species present are northern pike, largemouth bass, smallmouth bass, bluegills, black crappies, white crappies, rock bass, pumpkinseed, green sunfish, black bullheads, northern redhorse and bowfins. Carp, algal blooms and occasional fluctuating water levels are a problem to management of this impoundment. A quarter of a mile of frontage is in public ownership. This includes Champney Memorial Park-, Lamb's Creek Park (county), northwest public access (Northwest Rod and Gun Club),
another public access at Pine Point and four undeveloped platted accesses. Private development includes 16 resorts, three boat liveries, a trailer park camping area and 31 cottages and dwellings. Ten acres of marsh wetlands provide habitat for muskrats and nesting mallards, blue-winged teal and wood ducks. A number of diving ducks, coots and occasionally Canada geese are also found here during migration seasons. Source: 1962, Surface Water Resources of Dunn County Tainter Lake T29N, R12W, Sec. 7 Surface Acres = 1, 752.0, S. D. F. = 4.38, Maximum Depth = 37 feet

Date  1962

Author   Surface Water Inventory Of Wisconsin

Tainter Lake, Pine Creek and Red Cedar River,Wilson Creek Watershed (LC04) Fish and Aquatic LifeTainter Lake, Pine Creek and Red Cedar River,Wilson Creek Watershed (LC04) RecreationTainter Lake, Pine Creek and Red Cedar River,Wilson Creek Watershed (LC04) Fish Consumption

Impaired Waters

Tainter Lake (WBIC 2068000) was placed on the impaired waters list for total phosphorus in 1998. The TMDL for phosphorus was approved by the U.S. EPA in 2012. The 2018 assessments showed continued impairment by phosphorus; new total phosphorus and chlorophyll sample data exceeded 2018 WisCALM listing thresholds for the Recreation use and Fish and Aquatic Life use. Based on the most updated information, no change in the existing impaired waters listing was needed.

Date  2017

Author  Ashley Beranek

Impaired Waters

Tainter Lake (2068000) was placed on the impaired waters list for total phosphorus in 1998. The TMDL for phosphorus was approved by the U.S. EPA in 2012. The 2016 assessments showed continued impairment by phosphorus; total phosphorus sample data overwhelmingly exceeded 2016 WisCALM listing thresholds for the Recreation use and Fish and Aquatic Life use, and chlorophyll data overwhelmingly exceeded FAL thresholds and exceeded REC thresholds. Based on the most updated information, no change in existing impaired waters listing is needed.

Date  2015

Author  Aaron Larson

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

Shoreland Ordinance
Dunn County proposes to amend or create a shoreland zoning ordinance that complies with the requirements of NR 115, Wisconsin Administrative Code (as revised effective February 1, 2010) and retain existing regulations that exceed the water resource protections of NR 115 or are specific or unique to local needs.
Monitor Fish Tissue
TMDL (USEPA) Approved
EPA finds that the TP TMDLs for Tainter Lake and Lake Menomin satisfy all of the elements of an approvable TMDL. This approval is for 2 waterbody segments impaired by total phosphorus for a total of 2 TMDLs. These TMDLs address the eutrophication impairments on these lakes.
TMDL Implementation
Phosphorus TMDL Implementation for Lakes Menomin and Tainter. Implementation Plan is needed.
TMDL Implementation
Phosphorus TMDLs for Lakes Menomin and Tainter were completed in May 2012 and approved by the EPA on September 14, 2012. These "lakes" are impoundments of the Red Cedar River. The Red Cedar River drains portions of seven counties; land use is primarily agriculture which contributes to excess phosphorus leading to recreational impairments (unsightly blue-green algal blooms that limit wading, swimming and boating) in Lake Menomin and Tainter Lake. Please visit the UW-Extension Red Cedar River Watershed website for more information and details on outreach activites associated with the TMDL and the Lower Chippewa Basin.

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 Lake is located in the Wilson Creek watershed which is 244.75 miĀ². Land use in the watershed is primarily agricultural (37.50%), forest (31.40%) and a mix of grassland (19.40%) and other uses (11.70%). This watershed has 425.11 stream miles, 1,332.74 lake acres and 5,388.38 wetland acres.

Nonpoint Source Characteristics

This watershed is ranked High for runoff impacts on streams, High 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.This water is ranked High Lake for individual Impoundments based on runoff problems and the likelihood of success from project implementation.

Natural Community

Tainter Lake is considered a Reservoir 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.

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