Otter Creek, Sheboygan River Watershed (SH03)
Otter Creek, Sheboygan River Watershed (SH03)
Otter Creek (56400)
4 Miles
0 - 4
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-Warm Headwater
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.
2016
Fair
 
This river is impaired
Recreational Restrictions - Pathogens
E. coli
 
Sheboygan
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.
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.
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.
Default FAL
Fish and Aquatic Life - Default Waters do not have a specific use designation subcategory but are considered fishable, swimmable waters.

Overview

OTTER CREEK, SHEBOYGAN COUNTY
T15N R22E Sec. 7 NWNW Stream Length = 4.2 WBIC = 56400

Otter Creek, which originates at the outlet of a small privately owned spring lake, is 4.2 miles long, drains about 11 square miles and has an average gradient of 12.4 feet per mile. It flows southeast for a quarter mile through a white cedar and tamarack swamp until entering an area dominated by agriculture. The main stem of Otter Creek receives additional flow from the Gerber Lake outlet about 0.75 miles from its headwaters, and also from Little Elkhart Lake through a human-made outlet at the headwaters.

Otter Creek is the site of three major interrelated studies involving polluted runoff. The U.S. Geological Survey and WDNR have established a Whole Stream Monitoring site on Otter Creek at Willow Road which provides continuous monitoring of flow, dissolved oxygen, and temperature, along with storm flow monitoring. The DNR Bureau of Research is also using Otter Creek to fine tune the index of biotic integrity (IBI) so it will be more useful when making management decisions regarding sources of polluted runoff. Southeast Region DNR has also used Otter Creek to evaluate the performance of nonpoint source best management practices on sources of polluted runoff. The study involved three years of intensive evaluation monitoring to establish baseline data from which the effectiveness of the Nonpoint Source Pollution Abatement program could be determined. In addition, data were collected throughout the five-year implementation phase of the controls and collected for three years after implementation to track effectiveness.

An overview of the water quality of Otter Creek is presented here. Numerous publications have resulted from these nonpoint source evaluation monitoring studies and the reader is encouraged to examine these reports for additional information (e.g. Wierl et al. 1996, Wang et al. 1996, Rappold et al. 1997, Corsi et al. 1997, and Stuntebeck and Bannerman 1998). Otter Creek has a limited sport fish community, and diverse, relatively abundant forage fish community including species tolerant and very tolerant of pollution and degraded habitat. Although intolerant forage species are present, they are represented by fewer species and are less abundant. Northern pike from the Sheboygan River have been reported to use the stream and adjacent wetlands for spawning. Hilsenhoff biotic index (HBI) values from macroinvertebrate samples indicate good to fair water quality with respect to organic forms of pollution. The creek is only partially meeting its biological use potential for supporting a warm water forage fish community. Factors preventing Otter Creek from meeting its full potential include loss of in-stream and riparian habitat, excessive algae growth, and high concentrations of bacteria. Sources responsible include erosion from uplands and banks, streambank pasturing, livestock access to the stream, channelization, barnyard runoff and failing septic systems. Excessive sedimentation may reduce fish production because of loss of cover, poor spawning substrate, and the presence of few fish food organisms.

Date  2001

Author   Aquatic Biologist

Overview

OTTER CREEK, SHEBOYGAN COUNTY - T15N R22E Sec. 7, Stream Length = 4.2.
Otter Creek, which originates at the outlet of a small privately owned spring lake, is 4.2 miles long, drains about 11 square miles and has an average gradient of 12.4 feet per mile. It flows southeast for a quarter mile through a white cedar and tamarack swamp until entering an area dominated by agriculture. The main stem of Otter Creek receives additional flow from the Gerber Lake outlet about 0.75 miles from its headwaters, and also from Little Elkhart Lake through a human-made outlet at the headwaters.

Otter Creek is the site of three major interrelated studies involving polluted runoff. The U.S. Geological Survey and WDNR have established a Whole Stream Monitoring site on Otter Creek at Willow Road which provides continuous monitoring of flow, dissolved oxygen, and temperature, along with storm flow monitoring. The DNR Bureau of Research is also using Otter Creek to fine tune the index of biotic integrity (IBI) so it will be more useful when making management decisions regarding sources of polluted runoff. Southeast Region DNR has also used Otter Creek to evaluate the performance of nonpoint source best management practices on sources of polluted runoff. The study involved three years of intensive evaluation monitoring to establish baseline data from which the effectiveness of the Nonpoint Source Pollution Abatement program could be determined. In addition, data were collected throughout the five-year implementation phase of the controls and collected for three years after implementation to track effectiveness.

An overview of the water quality of Otter Creek is presented here. Numerous publications have resulted from these nonpoint source evaluation monitoring studies and the reader is encouraged to examine these reports for additional information (e.g. Wierl et al. 1996, Wang et al. 1996, Rappold et al. 1997, Corsi et al. 1997, and Stuntebeck and Bannerman 1998). Otter Creek has a limited sport fish community, and diverse, relatively abundant forage fish community including species tolerant and very tolerant of pollution and degraded habitat. Although intolerant forage species are present, they are represented by fewer species and are less abundant. Northern pike from the Sheboygan River have been reported to use the stream and adjacent wetlands for spawning. Hilsenhoff biotic index (HBI) values from macroinvertebrate samples indicate good to fair water quality with respect to organic forms of pollution. The creek is only partially meeting its biological use potential for supporting a warm water forage fish community. Factors preventing Otter Creek from meeting its full potential include loss of in-stream and riparian habitat, excessive algae growth, and high concentrations of bacteria. Sources responsible include erosion from uplands and banks, streambank pasturing, livestock access to the stream, channelization, barnyard runoff and failing septic systems. Excessive sedimentation may reduce fish production because of loss of cover, poor spawning substrate, and the presence of few fish food organisms.

Freshwater mussels are particularly sensitive to human induced changes in watersheds and are often used as one of many biological monitoring tools to assess the condition of the resource. WDNR conducted quantitative mussel surveys using the Random Point method in the Otter Creek subwatershed at sites where water chemistry, habitat, fish and macroinvertebrate data have been collected (Galarneau 1998). A population of the State Threatened Species slippershell mussel (Alasmidonta viridis) was found in the Otter Creek subwatershed. Specific collection sites are not reported for environmentally sensitive species (Endangered, Threatened, or Special Concern).

From: Galarneau, Steve and Masterson, John. 1999. Water Resources of the Sheboygan River Basin. Wisconsin Department of Natural Resources, Madison, WI.

Date  1999

Author   Aquatic Biologist

Otter Creek, Sheboygan River Watershed (SH03) Fish and Aquatic LifeOtter Creek, Sheboygan River Watershed (SH03) RecreationOtter Creek, Sheboygan River Watershed (SH03) Fish Consumption

General Condition

Hydrologic, water-quality, habitat, and fish data were collected at Otter Creek from 1990 to 2002 with the pre-BMP (best-management practice) period ending in September 1993 and the post-BMP period beginning in October 1999. BMPs installed in this basin included streambank protection and fencing, stream crossings, grade stabilization, buffer strips, various barnyard-runoff controls, nutrient management, and a low degree of upland BMPs. Reductions between pre- and post-BMP periods were detected in median concentrations of base-flow samples for total suspended solids and BOD5 but not for total phosphorus or dissolved ammonia nitrogen; fecal coliform concentrations in base-flow samples increased over the study period.

Date  2013

Author  Steve Corsi

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 to Evaluate Projects
determine if the water quality of Otter Creek has improved after the implementation of best management practices

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

Otter Creek is located in the Sheboygan River watershed which is 260.12 miĀ². Land use in the watershed is primarily agricultural (47.30%), grassland (17.60%) and a mix of wetland (16.70%) and other uses (18.30%). This watershed has 340.24 stream miles, 4,345.33 lake acres and 27,968.05 wetland acres.

Nonpoint Source Characteristics

This watershed is ranked Not Available for runoff impacts on streams, Not Available 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

Otter Creek is considered a 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.

Fisheries & Habitat

Freshwater mussels are particularly sensitive to human induced changes in watersheds and are often used as one of many biological monitoring tools to assess the condition of the resource. WDNR conducted quantitative mussel surveys using the Random Point method in the Otter Creek subwatershed at sites where water chemistry, habitat, fish and macroinvertebrate data have been collected (Galarneau 1998). The surveys were conducted using 1m2 quadrats randomly placed in three stream reaches. All mussels were collected within two quadrats randomly placed adjacent to each other across the stream channel. Both live and dead mussels (i.e. relict shells) were collected by hand, identified, enumerated and live specimens were returned to the stream. Environmentally sensitive mussel species (Endangered, Threatened or Special Concern) were measured and aged as well, and then returned to Otter Creek. Furthermore, a reference collection of shells was made to be used for educational benefits and to aid in future mussel identification. The non-environmentally sensitive mussel species collected at each site are identified below (Table 23). A population of the State Threatened Species slippershell mussel (Alasmidonta viridis) was found in the Otter Creek subwatershed. Specific collection sites are not reported for environmentally sensitive species (Endangered, Threatened, or Special Concern).

Date  2001

Author   Aquatic Biologist

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