Long Lake T34n R17w S06, Balsam Branch Watershed (SC05)
Long Lake T34n R17w S06, Balsam Branch Watershed (SC05)
Long Lake T34n R17w S06 (2478200)
273.34 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.
Shallow Seepage
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.
2024
Poor
 
This lake is impaired
Excess Algal Growth, Eutrophication
Total Phosphorus
 
Polk
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.
Restricted Aquatic Life
Fish and Aquatic Life communities are not fully supported in this ecosystem.
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.
Default FAL
Fish and Aquatic Life - Default Waters do not have a specific use designation subcategory but are considered fishable, swimmable waters.

Overview

Long Lake T34N, R17W, Sec. 6,7,8

A landlocked lake with fish species consisting of northern pike, largemouth bass, black crappies, perch, bluegills and bullheads. Public frontage includes a 66-foot access road with parking (west end), a 50-foot access road without parking (north side), two unimproved platted access roads (60 and 50 feet), and 125 feet of undeveloped frontage owned by the Town of Centuria. Private development consists of two resorts and 14 cottages. Main waterfowl use is limited to nesting mallards and bluewing teal.

Surface Acres = 257.0, S.D.F.= 2.01, Maximum Depth = 10 ft., M. P. A. = 68

Date  

Author   Aquatic Biologist

Historical Description

Long Lake is a 272 acre body of water with an intermittent outlet during high water periods. A
1981 feasibility study documented this lake as an eutrophic waterbody with watershed nutrient
loading a significant factor. Management alternatives included watershed improvements and
potential experimental in-lake alum "crib" treatment.
This lake should receive a priority for implementation work in the watershed. The past loading
to the lake may mask any short-term observable water quality improvements but the potential
for the development of new in-lake procedures may make this a reality in the future. The start
of a self-help monitoring program to track any water quality changes should be a high priority.
The possibility of a NPS Priority Lakes or Small Scale Watershed project should be explored.

Date  1992

Author   Surface Water Inventory Of Wisconsin

Long Lake T34n R17w S06, Balsam Branch Watershed (SC05) Fish and Aquatic LifeLong Lake T34n R17w S06, Balsam Branch Watershed (SC05) RecreationLong Lake T34n R17w S06, Balsam Branch Watershed (SC05) Fish Consumption

Impaired Waters

Long Lake (T34n R17w S06, WBIC 2478200) was placed on the impaired waters list for total phosphorus in 2014. 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

Long Lake T34n R17w S06 (2478200) was placed on the impaired waters list for total phosphorus in 2014. The 2016 assessments showed continued impairment by phosphorus; total phosphorus and chlorophyll sample data exceeded 2016 WisCALM listing thresholds for the Recreation use. Total phosphorus and chlorophyll data do not exceed Fish and Aquatic Life 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 2018. See also the 'monitoring and projects' tab.

Reports

Recommendations

Restore Riparian Habitat
Lakes Protection Grant
Long Lake P&R District is sponsoring a Lake Protection grant to protect and improve Long Lake water quality by designing and implementing shoreline restoration and runoff reduction practices. The project also includes an Alum dosage study.
Habitat Restoration - Shoreland
Shoreland Restoration
Best Management Practices, Implement
Nutrient Budget Development
Informational Meetings
Aquatic Plant Monitoring or Survey
Shoreland Monitoring, Assessment, Inventory
Shoreland Monitoring, Assessment or Inventory
Monitor or Assess Watershed Condition
Lakes Planning Grant
Lake Management Plan Development
Watershed Mapping or Assessment
Monitor Water Quality or Sediment

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

Long Lake is located in the Balsam Branch watershed which is 104.07 miĀ². Land use in the watershed is primarily forest (31.60%), agricultural (28.40%) and a mix of grassland (18.70%) and other uses (21.30%). This watershed has 63.62 stream miles, 6,301.67 lake acres and 5,248.51 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.This water is ranked High Lake for individual Lakes based on runoff problems and the likelihood of success from project implementation.

Natural Community

Long Lake T34n R17w S06 is considered a Shallow Seepage 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.

Shallow seepage lake describes the depth and location of the lake in a watershed. These variables affect the lakes response to watershed variables.