Sinissippi Lake (Hustisford), Sinissippi Lake Watershed (UR08)
Sinissippi Lake (Hustisford), Sinissippi Lake Watershed (UR08)
Sinissippi Lake Beach, Neider Park Landing (859900)
0.40 Miles
0 - 0
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's Riverine Natural Communities.
Reservoir
Year Last Monitored
This date represents the most recent date of water quality monitoring stored in the SWIMS system. Additional field surveys for fish and habitat may be available subsequent to this date.
2017
Unknown
 
Dodge
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.
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.
Reservoir
Reservoir
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.
FAL
Fish and Aquatic Life - waters that do not have a specific use designation subcategory assigned but which are considered fishable, swimmable waters.
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

Sinissippi Lake is a 2,855-acre impoundment of the Rock River in Dodge County. Historically, this was a rapids area of the Rock River before the stretch was dammed. The lake has a maximum depth of 8 feet, with an average depth of 4.5 feet. It is a shallow eutrophic to hypereutrophic lake and supports multiple uses. Its drainage area is about 511 square miles. Because it is an impoundment with a large drainage area, it has water quality problems associated with impoundments in southern Wisconsin. These problems are turbidity, decreased habitat and periodic decreased DO levels (Eagan, 1989). Most of these problems are caused by polluted runoff in its drainage area. Heavy stormwater runoff due to intense farming and the loss of wetlands has increased soil erosion, sediment, and nutrient delivery to the lake. Excessive rough fish populations also afflict the lake. The fishery is now dominated by carp and bullhead, although there is a moderate population of walleye and a small population of northern pike. The lakeshore is significantly developed like most other lakes in southern Wisconsin. However, large stretches of lake shore remain undeveloped. In 1999, a pair of Bald eagles established a nest on lake shore property and sucessfully raised young in 2001.

The increased number of power boats on the lake and the Rock River immediately above the lake may also be causing water quality problems by resuspending fine bottom sediments and causing bank erosion. The lake could be a valuable migration stop for waterfowl. However, intensive use limits hunting opportunities.

In 2000, the Lake Sinissippi Management District was formed. The District has developed a comprehensive lake management plan with various management components to implement over the next five years. In 2001, the Lake Sinissippi Lake Improvement Association received a Lakes Protection Grant to monitor nutrient and sediment loading to the lake from the Rock River and Dead Creek. Another monitoring station will monitor the water quality leaving the lake at Hustisford. The monitoring will complement earlier, similar water quality monitoring conducted at Horicon and Hustisford by the Lake Sinnissippi Association, the Rock River Partnership, the Rock River Headwaters, the Village of Hustisford and the Town of Hubbard.

Date  2002

Author   Aquatic Biologist

Historical Description

A large, shallow impoundment of the Rock River, created by a 12-foot dam at Hustisford. Known as Hustis' Rapids, the site was considered the finest waterpower on the river between Mayville and Rockford, Illinois. The original dam was erected in 1845. The lake flooded a sprawling, marshy valley and the numerous drumlins form peninsulas and islands as well as portions of the shoreline. The nearly level, peat bottomed depression did not lend itself to the formation of a deep reservoir and subsequent siltation from the watershed coupled with deposition from deteriorating marshes contributed to the shallowness. In 1939, the dam was raised, and water levels increased by 1.43 feet. This resulted in further breakup of the marshes. Today silt is the predominant bottom material and the lake varies between 3 and 4 feet in depth.

The shallow, fertile environment proved well suited for carp, and in 1939 the Wisconsin Conservation Department installed a fish trap on the Rock River north of the main body of the lake to control the population. The water is usually turbid and heavy algae blooms are a common occurrence. Because the lake is fed from Horicon Marsh waters poor in oxygen, winterkills are the rule and seldom does a winter pass without at least a partial kill. Addition of nutrients from sewage plants located within the immediate drainage area adds to the previously mentioned problems. The fishery consists mainly of carp, bullheads and northern pike, the latter species providing excellent fishing upon occasion. Large size and tendency to freeze-out makes the lake very difficult to manage, and fishing is spotty due to natural fluctuations. Exchange of fish populations occur with both the Horicon Marsh and the river below Hustisford. During the spring migration large numbers of waterfowl visit the lake, and at times 3,000 ducks,5,000 geese, and 500 swans have been observed. Lesser numbers stop in autumn, and heavy hunting pressure soon drives most of the birds to the Horicon Marsh.

The 2,300 acre lake has great potential for boating, and boating use has increased rapidly in recent years. Swimming conditions are poor due to the depth and quality of the water, algae, and soft bottom. A boat ramp located near the dam in a Hustisford park provides access, although parking is limited. Many boaters put in at either of two parks in Horicon and cruise the 4-mile stretch of the river to the lake. Hundreds of cottages and homes are located on the 17 miles of shoreline, and recent large-scale developments have added many to those already present. Extensive marshes remain along the north and west shores, and still produce significant numbers of muskrat and waterfowl.

The problems of siltation and pollution may someday be relieved, and a selective poison will provide a means of controlling the rough fish. Winterkill potential will always remain, a result of physical limitations alone. A complete drawdown has been suggested to expose the muck and enhance bottom compaction and oxidation of vegetative growth. Conflict of interest between hunter, fisherman, boater and cottage owner makes planning of solutions difficult under present conditions. Source: 1965, Surface Water Resources of Dodge County Sinissippi Lake T10, 11N, R16E Surface Acres = 2,300, S.D.F. = 2.53, Maximum Depth = 5 feet

Date  1965

Author   Surface Water Inventory Of Wisconsin

Sinissippi Lake (Hustisford), Sinissippi Lake Watershed (UR08) Fish and Aquatic LifeSinissippi Lake (Hustisford), Sinissippi Lake Watershed (UR08) RecreationSinissippi Lake (Hustisford), Sinissippi Lake Watershed (UR08) Fish Consumption

Impaired Waters

Sinissippi Lake (WBIC 859900) was placed on the impaired waters list in 2006 for total phosphorus and sediment/total suspended solids. The TMDL for both of these pollutants was approved by the U.S. EPA in 2011. The 2018 assessments showed continued impairment by phosphorus; new total phosphorus and chlorophyll-a sample data exceeded the 2018 WisCALM listing thresholds for the Recreation use and Fish and Aquatic Life use. Based on the most updated information, no change in the existing impaired waters listing was needed.

Date  2017

Author  Ashley Beranek

Impaired Waters

Sinissippi Lake (859900) was placed on the impaired waters list in 2006 for total phosphorus and sediment/total suspended solids. The TMDL for both of these pollutants was approved by the U.S. EPA in 2011. The 2016 assessments showed continued impairment by phosphorus; total phosphorus sample data overwhelmingly exceeded 2016 WisCALM listing thresholds for the Recreation use and Fish and Aquatic Life use, and chlorophyll data overwhelmingly exceeded FAL thresholds and exceeded REC thresholds. 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 2016 . See also 'monitoring' and 'projects'.

Reports

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 and implementation of a Total Maximum Daily Load Analysis, habitat restoration work, partnership education and outreach and more. If specific recommendations exist for this water, they will be displayed below.

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

Sinissippi Lake (Hustisford) is located in the Sinissippi Lake watershed which is 234.93 miĀ². Land use in the watershed is primarily agricultural (71%), wetland (12%) and a mix of suburban (7%) and other uses (10%). This watershed has 458.18 stream miles, 1,917.70 lake acres and 22,222.24 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.

Natural Community

Sinissippi Lake Beach, Neider Park Landing is considered a Reservoir under the state's Natural Community Determinations.

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's Riverine Natural Communities.

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