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Warm Headwater, Cool-Cold Headwater, COOL-Warm Headwater
Fish and Aquatic Life
The origin of Brighton Creek is in the northeast one-quarter of Section 14, Township 2 North, Range 20 East, Town of Brighton. From its origin, the Creek flows about six miles in a generally southerly direction, to its confluence with the Salem Branch of Brighton Creek in the southwest one-quarter of Section 6, Township 1 North, Range 21 East, Town of Bristol; then about three miles in a generally northeasterly direction, to its confluence with the Des Plaines River in the southwest one-quarter of Section 33, Township 2 North, Range 21 East. Brighton Creek has a perennial stream length of about nine miles.
Author Aquatic Biologist
Brighton Creek was assessed during the 2018 listing cycle; new biological (macroinvertebrate Index of Biotic Integrity (IBI) scores) 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.
Author Ashley Beranek
Brighton Creek is a 13-mile long tributary to Des Plaines River. Its current use is listed as supporting fish and other aquatic life and its attainable use is as a warm water sport fishery.
Author Aquatic Biologist
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.
Monitor Water Quality or Sediment
Category 2. 2018 TP Results: May Exceed. Station: 10008154. AU: 10422.
Brighton Creek should be considered as a high priority for selection of non-point source management projects and funding.
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 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
|WBIC||Official Waterbody Name||Station ID||Station Name||Earliest Fieldwork Date||Latest Fieldwork Date||View Station||View Data|
|737400||Brighton Creek||10008260||Brighton Creek at Hwy 45||Map||Data|
|737400||Brighton Creek||10013693||Brighton Creek Downtream Of 18th St||Map||Data|
|737400||Brighton Creek||10020799||Brighton Creek-Riffle 80 M Ds Of K||Map||Data|
|737400||Brighton Creek||10010490||Brighton Creek 6||Map||Data|
|737400||Brighton Creek||303049||Brighton Creek at Cth K (Bi Sur)||5/19/1979||1/1/2015||Map||Data|
|737400||Brighton Creek||10008121||Brighton Creek (Ush 45)||11/8/1999||11/16/2001||Map||Data|
|737400||Brighton Creek||10011247||Brighton Creek at Hwy K (60th St) (47m Upstream)||Map||Data|
|737400||Brighton Creek||10020781||Brighton Creek-Riffle 10 M Ds Of Beaver Dam Pond||Map||Data|
|737400||Brighton Creek||10008154||Brighton Creek - 45th St.||10/9/2007||11/6/2015||Map||Data|
Brighton Creek is located in the Des Plaines River watershed which is 133.34 mi². Land use in the watershed is primarily agricultural (57.90%), suburban (11%) and a mix of wetland (8.90%) and other uses (22.30%). This watershed has 216.36 stream miles, 755.01 lake acres and 7,194.07 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.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.
Brighton Creek is considered a Warm Headwater, Cool-Cold Headwater, COOL-Warm Headwater under the state's Natural Community Determinations.
Natural communities (stream and lake natural communities) represent model resultsand 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 (Warm-Transition) Headwaters are small, sometimes intermittent streams with cool to warm summer temperatures. Coldwater fishes are uncommon to absent, transitional fishes are abundant to common, and warm water fishes are common to uncommon. Headwater species are abundant to common, mainstem species are common to absent, and river species are 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.
Warm Headwaters are small, usually intermittent streams with warm summer temperatures. Coldwater fishes are absent, transitional fishes are common to uncommon, and warm water fishes are abundant to common. Headwater species are abundant to common, mainstem species are common to absent, and
river species are absent.
More Interactive Maps
Maps of Watershed