0 - 5.55
Cool-Cold Headwater, Coldwater
Fish and Aquatic Life
Halls Valley Creek, also known as Creek 32-9, is a small spring-fed stream located in southwestern Monroe County. It flows in an easterly direction for approximately four miles before reaching the Little La Crosse River north of Melvina. Halls Valley Creek has a gradient of 71 feet per mile and drains moderately steep agriculture land and wooded hillsides. Halls Valley Creek is a Class I trout stream for its entire length.
The most recent survey, completed in 1974, documented cool, clear water with a stream bottom consisting predominately of rubble with lesser amounts of sand, silt, gravel, and boulder. The most abundant in-stream cover for fish was boulders, while undercut banks, logs and trees, and aquatic vegetation were generally scarce. Riparian land consisted of mainly upland hardwoods with lesser amounts of cultivated land, pasture and open marsh. Brook trout, brown trout and several forage fish species were collected. The presence of brook and brown trout fingerlings suggest the occurrence of natural reproduction. The Halls Valley Creek fishery would benefit from additional in-stream cover. A fish and habitat survey of Halls Valley Creek should be conducted to document the current status of the stream. There are no DNR stocking records for Halls Valley Creek. Access to this stream is available from one bridge crossing and DNR owned easements.
Author Aquatic Biologist
Halls Valley Creek (1657600) was assessed during the 2018 listing cycle; new biological (fish 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
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.
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
|Project Name (Click for Details)||Year Started|
|WBIC||Official Waterbody Name||Station ID||Station Name||Earliest Fieldwork Date||Latest Fieldwork Date||View Station||View Data|
|1657600||Unnamed||10014175||Unnamed (Halls Valley) Cr (Cr. 32-9) Station1 Lamplighter Rd. Bridge||1/1/2015||8/29/2022||Map||Data|
|1657600||Unnamed||10014174||Halls Valley Cr. (Cr. 32-9) Station 4 - Farm Rd. Bridge Crossing In Nw 1/4 Of S2||Map||Data|
|1657600||Unnamed||10013149||Creek 32-9 (Halls Valley) St. 1-05 100 Meters Downstream Of Farm Bridge||1/1/2015||1/1/2015||Map||Data|
|1657600||Unnamed||10014172||Halls Valley Cr. (Cr. 32-9) Station 1 - North Of Cth F Sharp Bend In S32||Map||Data|
|1657600||Unnamed||10014379||Halls Valley Creek (Cr. 32-9) Station 12 - West Of The Junction Of Lamplighter Rd. And A Farm Rd.||Map||Data|
|1657600||Unnamed||10014173||Halls Valley Cr. (Cr. 32-9) Station 2- Farm Rd. Bridge Crossing In Sw 1/4 Of S33||Map||Data|
|1657700||Unnamed||10014179||Cr. 4-1 Station 2a - Mouth Upstream||Map||Data|
|1657600||Unnamed||10022460||Halls Valley Cr. (Cr. 32-9) - 150m Upstream Of Linefence||1/1/2015||1/1/2015||Map||Data|
|1657800||Unnamed||10014177||Cr. 3-7 Station 3 - Cth F Bridge Crossing In Ne 1/4 Of S3||Map||Data|
|1657800||Unnamed||423025||Halls Valley Creek Trib at Cth F||Map||Data|
Unnamed is located in the Little La Crosse River watershed which is 240.79 mi². Land use in the watershed is primarily forest (48%), agricultural (25.70%) and a mix of grassland (15.60%) and other uses (10.80%). This watershed has 445.88 stream miles, 114.59 lake acres and 5,439.88 wetland acres.
Nonpoint Source Characteristics
This watershed is ranked High for runoff impacts on streams, Not Ranked for runoff impacts on lakes and Low for runoff impacts on groundwater and therefore has an overall rank of Low. 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.
Halls Valley Creek (T16n R3w S32)(Unnamed Creek 32-9) is considered a 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) 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.