Lemonweir River, Lower Lemonweir River Watershed (LW27)
Lemonweir River, Lower Lemonweir River Watershed (LW27)
Lemonweir River (1301700)
20.18 Miles
0 - 20.18
Macroinvertebrate, Cool-Cold Headwater, Coldwater, Cool-Warm Headwater, Large River
2024
Poor
 
This river is impaired
Impairment Unknown
Total Phosphorus
 

Overview

Lemonweir River - The Lemonweir River in the Lower Lemonweir River Watershed - LW27)
extends from its confluence with the Wisconsin River
upstream to the dam at New Lisbon. The river has a diverse warm water sport fishery. The
dominant gamefish in this reach is the smallmouth bass. Streambank erosion is a problem in
this reach, resulting in sand and sediment accumulating in the deeper holes and backwater
areas, and increased turbidity. It is believed that the proposed removal of the Lemonweir Mill
Dam would eliminate backwater spawning and nursery areas.

Lemonweir River in the Little Lemonweir River Watershed (LW29) - The Lemonweir River flows
through eastern Monroe County and west central Juneau County
in a southeasterly direction for 56 miles before reaching the Wisconsin River between Castle
Rock Lake and the Wisconsin Dells. The Lemonweir River in this watershed extends from the
dam in New Lisbon upstream to where the South and East Forks of the Lemonweir River
converge at Wyeville. These upper 25 miles of the Lemonweir River support a warm water
sport fishery comprised of northern pike, walleye and panfish. The river is bordered by
hundreds of wetland acres and agricultural lands. From Wyeville downstream past the
confluence of Bear Creek, the Lemonweir River has been straightened. However, a low
gradient of only three feet per mile in Juneau County creates a meandering river down to New
Lisbon which can be difficult to navigate. Since the last biological survey was conducted in
1966, a fish and habitat survey should be conducted on the Lemonweir River upstream of
New Lisbon to document existing conditions. Access to the Lemonweir River upstream of
New Lisbon is from seven road crossings. The WDNR has been purchasing easements along
sections of the river to establish riparian buffers to improve stream health.

Ripp, Coreen, Koperski, Cindy and Folstad, Jason. 2002. The State of the Lower Wisconsin River Basin.
PUBL WT-559-2002. Wisconsin Department of Natural Resources, Madison, WI.

Date  2002

Author  Cynthia Koperski

Historical Description

The Lenaonweir River in this watershed extends from its confluence with the Wisconsin
Rives upstream to dam at New Lisbon. The river has a diverse warm water sport fishery.
The dominant gamefish in this reach is the smallrrlouth bass (WDNR, 1991).
Streambank erosion is a problem in this reach, resulting in sand and sediment
accumulating in the deeper holes and backwater areas, and increased turbidity
(Ironside, 1991). It is believed that the proposed removal of the Lemonweir Mills dam
would eliminate backwater spawning and nursery areas (WDNR, 1991).

Date  1994

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.
Fish and Aquatic Life - Default Waters do not have a specific use designation subcategory but are considered fishable, swimmable waters.