8.66 Miles
15 - 23.66
Cool-Warm Mainstem, Cool-Warm Headwater
2015
Good
Jackson
Yes
No
No
Fish and Aquatic Life
Overview
Robinson Creek flows 25 miles before reaching the Black River between Melrose and Black River Falls. This stream historically supported an outstanding Class I trout fishery. The current classifications, Class II and Class III, illustrates the loss of reproduction in the trout population. Numerous impoundments used in the cultivation of cranberries in the tributaries and headwaters of this stream have likely increased average stream temperatures above the threshold for trout reproduction. The Department no longer stocks trout in Robinson Creek. If the headwater and tributary impoundments were removed, this stream may once again attain Class I status (Talley). In 1992, Robinson Creek water was sampled downstream of commercial cranberry marsh complexes on three separate occasions. On one occasion, the water caused complete mortality of two aquatic insect test species. Chemical analysis of the water documented the insecticide diazinon in concentrations adequate to cause the mortality (Schreiber).
From: Koperksi, Cindy. 1999. Black River Water Quality Management Plan (draft). Wisconsin Department of Natural Resources, Madison, WI.
Date 1999
Author Cynthia Koperski
Impaired Waters
Robinson Creek (1696300), from the mouth to about a mile west of Hwy I Rd, was placed on the impaired waters list for total phosphorus in 2012. The 2016 assessments showed continued impairment by phosphorus; total phosphorus sample data exceed 2016 WisCALM listing criteria for the Fish and Aquatic Life use, however, available biological data do not indicate impairment (i.e. no macroinvertebrate or fish Index of Biotic Integrity (IBI) scored in the "poor" condition category). This water was also assessed for temperature and sample data did not exceed 2016 WisCALM listing criteria for the Fish and Aquatic Life use. 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
Monitor Aquatic Biology
Conduct biological monitoring on Robinson Creek wbic 1696300 by 2018.
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
WBIC | Official Waterbody Name | Station ID | Station Name | Earliest Fieldwork Date | Latest Fieldwork Date | View Station | View Data |
---|
1696300 | Robinson Creek | 10039640 | Robinson Creek NW of CTH O and Hableman Rd | 5/20/2009 | 5/20/2009 | Map | Data |
1696300 | Robinson Creek | 10038969 | Robinson Creek - County Highway O upstream | | | Map | Data |
1696300 | Robinson Creek | 273033 | Robinson Creek - Cth O | 5/13/1992 | 10/4/2001 | Map | Data |
1696300 | Robinson Creek | 10008520 | Ne Corner Of 1st Parking Lot At Robinson Beach | | | Map | Data |
1696300 | Robinson Creek | 10008519 | End Of Woods Rd | 1/1/2015 | 1/1/2015 | Map | Data |
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Watershed Characteristics
Robinson Creek is located in the Trout Run and Robinson Creeks watershed which is 216.93 miĀ². Land use in the watershed is primarily forest (72.30%), agricultural (11%) and a mix of wetland (6.70%) and other uses (10.00%). This watershed has 326.05 stream miles, 791.85 lake acres and 17,562.31 wetland acres.
Nonpoint Source Characteristics
This watershed is ranked High for runoff impacts on streams, Not Available 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.
Robinson Creek is considered a Cool-Warm Mainstem, Cool-Warm Headwater 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 (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.