Tipperary Creek, Allen Creek and Middle Sugar River Watershed (SP13)
Tipperary Creek, Allen Creek and Middle Sugar River Watershed (SP13)
Tipperary Creek (885400)
5.70 Miles
0 - 5.70
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, 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.
2022
Excellent
 
Green
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.
No

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.
Supported Aquatic Life
Waters that support fish and aquatic life communities (healthy biological communities).
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 II Trout)
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.
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

From: Poff, Ronald J., and C.W. Threinen, Lake and Stream Classification Project. Surface Water Resources of Green County, Wisconsin Conservation Department, Madison I, 1961.

Story Creek is a spring-fed tributary to the Sugar River originating in south central Dane County and joining the Sugar River in Green County. A great deal of the stream runs through the Brooklyn State Wildlife Area. Streambank erosion and beaver dams near the stream’s headwaters have impacted the trout habitat in the upper portion (Surface Waters of Dane Co.). The lower 6.6 miles is managed as a Class II trout fishery, classified as an ERW, and is considered one of the best trout streams in Green County (Water Resources of Green County). Additionally, some warm water species such as northern pike and panfish are found in some of the ditched sections (Surface Waters of Dane Co.).
The entire stream has been impacted by agricultural runoff and is likely achieving its highest potential use (Bush, pers comm). Two major trout stamp projects have been done in recent years to rehabilitate three-quarters of a mile of stream. Fish and habitat surveys conducted in the last several years show the stream supports both reproducing populations of brook and brown trout as well as cool water forage species.

Date  

Author   Aquatic Biologist

Overview

Story Creek is a spring-fed tributary to the Sugar River originating in south central Dane County and joining the Sugar River in Green County. A great deal of the stream runs through the Brooklyn State Wildlife Area. Streambank erosion and beaver dams near the stream’s headwaters have impacted the trout habitat in the upper portion (WDNR, 1985). The lower 6.6 miles is managed as a Class II trout fishery, classified as an ERW, and is considered one of the best trout streams in Green County (WDNR, 1980a). Additionally, some warm water species such as northern pike and panfish are found in some of the ditched sections (WDNR, 1985).

The entire stream has been impacted by agricultural runoff and is likely achieving its highest potential use (Bush, 2001). Two major trout stamp projects have been done in recent years to rehabilitate three-quarters of a mile of stream. Fish and habitat surveys conducted in the last several years show the stream supports both reproducing populations of brook and brown trout as well as cool water forage species.

Date  2002

Author   Aquatic Biologist

Historical Description

Story Creek (Tipperary Creek) -T5N, R8E, Sec. 36, Surface acres = 6.5, Length =3 miles, Stream order = II, Gradient = 8.7 ft/mile, Base discharge = 8.9 cfs. (7.5 stream miles total including portion in Green County)
Story Creek is a sprlng-fed tributary to the Sugar River originatlng in south central Dane County and
joining the Sugar River in Green County near Dayton. It is located within the Brooklyn Wildlife Area and drains 27 square miles (Dane and Green Counties) of agricultural and marsh lands. Much of the agricultural land has been created by draining these peat marshes and ditching the creek. One effect of these alterations is a lowering of the water table and a resultant reduction in stream flow (Dane Cty. Reg. Plann. Comm. 1979a). Stream bank erosion is a significant problem and beaver dams near the creek's headwaters have ruined most of the trout habitat in the upper part of the stream. Despite these problems Story Creek is a Class II trout stream. Most of the stream is located in Green County. Its 12 feeder springs keep the waters cool and the substrate composition in some portions is favorable spawning habitat for brown trout. In addition, both brook and brown trout are stocked. Northern pike are common in the ditched stretches, along with diverse groupings of panflsh and forage fish.
Story Creek is not affected by any industrial or municipal wastes, and its waters are of good quality. Agricultural runoff and stream bank erosion are the only significant causes of pollution (Dane Cty.Reg. Plann. Comm. 1979a). Public access to the creek is good within the Brooklyn Wildlife Area. Its recreational value is high owing to its wildlife resources, that include pheasant, duck, quail, deer, rabbit, woodcock, and squirrel. The Brooklyn Wildlife AreaiIs one of the most popular hunting sites in Dane County.
The channelized portions have little aesthetic value. The stream has the potential to produce more wild trout. Fish species: American brook lamprey, brown. brook. and rainbow trout, central mudminnow, central stoneroller, redside dace, fathead minnow, blacknose dace, creek chub, white sucker, golden and shorthead redhorse, brook stickleback, green sunfish, rainbow, Iowa, fantail and johnny darter, mottled sculpin. and northern pike.

From: Day, Elizabeth A.; Grzebieniak, Gayle P.; Osterby, Kurt M.; and Brynildson, Clifford L., 1985. Lake and Stream Classification Project. Surface Water Resources of Dane County, Wisconsin Department of Natural Resources, Madison, WI.

Date  1985

Author   Surface Water Inventory Of Wisconsin

Historical Description

Flows south along the town line and southwest into the Sugar River. Managed for brown trout; however, smallmouth bass are common. Much clear deep water with sand and gravel bottoms; silt at a minimum. Accessible through public hunting grounds. Rainbow trout are planted here annually. One hundred and twenty-five acres of predominantly open marsh lies contiguous with the stream. From: Poff, Ronald J., and C.W. Threinen, Lake and Stream Classification Project. Surface Water Resources of Green County, Wisconsin Conservation Department, Madison I, 1961.Surface Acres= 10.9, Miles= 4.5, Gradient- 17.8' per mile

Date  1961

Author   Surface Water Inventory Of Wisconsin

Tipperary Creek, Allen Creek and Middle Sugar River Watershed (SP13) Fish and Aquatic LifeTipperary Creek, Allen Creek and Middle Sugar River Watershed (SP13) RecreationTipperary Creek, Allen Creek and Middle Sugar River Watershed (SP13) Fish Consumption

General Condition

Story Creek [Tipperary] (Mile 0 to 12.54) was assessed during the 2018 listing cycle; new biological (fish Index of Biotic Integrity (IBI) scores) and temperature sample data were clearly below the 2018 WisCALM listing thresholds for the Fish and Aquatic Life use. This water was meeting this designated use and was not considered impaired.

Date  2017

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

Story Creek is located in the Allen Creek and Middle Sugar River watershed which is 154.01 miĀ². Land use in the watershed is primarily agricultural (61.50%), grassland (17.30%) and a mix of forest (9.30%) and other uses (11.80%). This watershed has 263.25 stream miles, 96.10 lake acres and 5,963.23 wetland acres.

Nonpoint Source Characteristics

This watershed is ranked Medium 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

Tipperary Creek is considered a Cool-Cold Mainstem, 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.

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