Como Lake, Duncan Creek Watershed (LC18)
Como Lake, Duncan Creek Watershed (LC18)
Como Lake (2152100)
98 Acres
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.
Reservoir
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.
2019
Fair
 
This impoundment is impaired
High Phosphorus Levels, Excess Algal Growth
Total Phosphorus
 
Chippewa
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.
Shallow Lowland
Shallow lowland lake describes the depth and location of the lake in a watershed. These variables affect the lakes response to watershed variables.
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.
Default FAL
Fish and Aquatic Life - Default Waters do not have a specific use designation subcategory but 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.
Cold
Streams capable of supporting a cold water sport fishery, or serving as a spawning area for salmonids and other cold water fish species. Representative aquatic life communities, associated with these waters, generally require cold temperatures and concentrations of dissolved oxygen that remain above 6 mg/L. Since these waters are capable of supporting natural reproduction, a minimum dissolved oxygen concentration of 7 mg/L is required during times of active spawning and support of early life stages of newly-hatched fish.

Overview

These Duncan Creek impoundments are generally shallow, eutrophic, and support a warm water fishery. The impoundments have very high nutrient levels that result in nuisance growth of duckweed and excessive sedimentation that is filling in the impoundments. The impoundments are included in the Duncan Creek Priority Watershed Program, whch will control sources of polluted runoff. Reductions in sediment delivery will lengthen the useful life of the impoundments. It is unlikely that nutrient inputs can be reduced enough through the priority watershed project to result in decreased growth of duckweed (Schreiber 1992). The submergent aquatic plants of these impoundments are limited to species adapted to low light, eutrophic conditions and high siltation rates. These lakes also contain large mats of duckweed covering more than half the surface area at times. Physical removal of duckweed and harvesting of other aquatic plants are management options for control of nuisance levels of rooted aquatic plants (Borman) .

Date  1996

Author   Aquatic Biologist

Historical Description

Source: 1963, Surface Water Resources of Chippewa County Lake Como T30N, R9W, Sections 5 and 6

A soft water, drainage impoundment on Duncan Creek. It has an 11-foot water control structure on its outlet owned by the Bloomer Farm Products Co. Its fish population consists of largemouth bass and pan fish. Muskrats are common and mallardsand blue-winged teal use the flowage area for nesting. There is a one-half acre City of Bloomer park on its east shore with facilities for swimming and access. There are three other undeveloped platted roads to the flowage for a total of 0.11 miles of public frontage. Private development consists of 34 homes.

Surface Acres = 97.9, S.D.F. = 3.76, Maximum Depth = 6 feet

Date  1963

Author   Surface Water Inventory Of Wisconsin

Como Lake, Duncan Creek Watershed (LC18) Fish and Aquatic LifeComo Lake, Duncan Creek Watershed (LC18) RecreationComo Lake, Duncan Creek Watershed (LC18) Fish Consumption

Impaired Waters

Como Lake was recently evaluated during the ten-year period of 2009 through 2018 for results that were reported to the USEPA for the 2020 Clean Water Act condition report. The waterbody is considered impaired, or in poor condition for designated uses which include the quality of fish and aquatic life, recreational use, and public health and welfare (fish consumption and related). Pollutants or problems encountered during sampling (impairments) are determined based on water quality standards outlined in Wisconsin 2020 Consolidated Assessment and Listing Methodology (WisCALM). Assessment results show water conditions that are potentially harmful for Recreation use due to values for total phosphorus and chlorophyll that fall into the range expected for an aquatic community in poor health, therefore this water is listed as impaired.

Assessment results during the 2020 listing cycle show excess algal growth as a result of total phosphorus levels. Chlorophyll and total phosphorus data were assessed during the 2020 listing cycle. Both were too high for the Recreation designated use; however results for Aquatic Life were less clear and may exceed listing criteria. Based on the most updated information, this water was proposed for the impaired waters list in 2020.


Date  2019

Author  Ashley Beranek

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

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

Como Lake (Bloomer Mill Pond) is located in the Duncan Creek watershed which is 191.44 miĀ². Land use in the watershed is primarily agricultural (44.40%), forest (21%) and a mix of grassland (13.90%) and other uses (20.70%). This watershed has 270.37 stream miles, 185.45 lake acres and 6,971.50 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

Como Lake is considered a Reservoir 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.

More Interactive Maps