Hallie Lake, Duncan Creek Watershed (LC18)
Hallie Lake (2150200)
78.64 Acres
Reservoir
2024
Poor
 
This is impaired
Degraded Habitat, Elevated pH
Mercury, Total Phosphorus, Sediment/Total Suspended Solids
 

Overview

Lake Hallie is a 79-acre oxbow lake formed by the Chippewa River. The lake is managed for both
warm and cold water fisheries. The lake experiences nuisance growths of elodea, curly-leaf
pondweed, algae and duckweed. Lake Hallie has a diverse aquatic plant community dominated by
elodea. Nuisance ~ l a n t growth likely could be controlled through reducing nutrient inputs and
harvesting rooted plants.
Lake Hallie currently has an average total phosphorus concentration of 30 micrograms per liter
(ug/l). This phosphorus concentration is relatively high for natural lakes. The potential for reducing
the phosphorus concentration through controlling watershed inputs should be evaluated. It is
important that best management practices be implemented through the Duncan Creek Priority
Watershed Project, whch will protect and improve water quality in Lake Hallie (Schreiber 1992).

Date  1996

Author   Aquatic Biologist

Historical Description

Source: 1963, Surface Water Resources of Chippewa County Lake Hallie T28N, R9W, Sections 26 and 27

A soft water, drainage impoundment with a sizeable outlet to the Chippewa River. A large spring area on the northeast part of the lake contributes to the outlet flow. Its outlet has two water control structures of 10 feet and 5 feet owned by Mrs. George Reever. Considered to be a bass pan fish lake, it has largemouth bass, northern pike, bullheads, bluegills, black crappies, pumpkinseeds, white suckers, and carp. Management problems of the lake are its carp population and an occasional partial winterkill. Only migratory ducks and a few coots use the lake as a resting area. Muskrats are common. Private development consists of 11 cottages with one boat rental place. Public frontage and access consists of a town road bordering the lake outlet.

Surface Acres = 80.0, S.D.F. = 3.75, Maximum Depth = 14 feet

Date  1963

Author   Surface Water Inventory Of Wisconsin

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.
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.
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.
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.
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.
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.
Fish and Aquatic Life communities are not fully supported in this ecosystem.
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.
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.
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.
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.