Water Detail - Nederlo Creek, Reads and Tainter Creeks Watershed (LW03)

Nederlo Creek, Reads and Tainter Creeks Watershed (LW03)

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Nederlo Creek (1185700)

Size

3.90 Miles

Segment

2.75 - 6.65

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.

Cool-Cold Headwater

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

General Condition

Good

County

Crawford

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.

Yes

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.

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.

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.

Supported Aquatic Life

Waters that support fish and aquatic life communities (healthy biological communities).

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.

Cold (Class II Trout)

Streams 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 through natural reproduction and selective propagation. 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.

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

Nederlo Creek, also known as Johnstown Creek, is located in north central Crawford County.
This stream flows in a north easterly direction for 4.1 miles before reaching Tainter Creek
north of Gays Mills. Nederlo Creek has a gradient of 27 feet per mile and drains forested
hillsides and agricultural valleys. Nederlo Creek is a Class II trout stream upstream of
Freeman Road for 2.1 miles and Class III downstream of Freeman Road for 2.0 miles.
The most recent survey, conducted in 1998, documented a small brown trout population and a
very diverse community of forage fish species. At the time, sand and silt made up nearly 50%
of the stream bottom followed by cobble (41%) and small amounts of gravel and boulder. The
majority of in-stream cover consisted of aquatic vegetation and some boulders. Habitat seems
to be the limiting factor for trout in Nederlo Creek. Streambank pasturing of livestock contributes
greatly to the sediment problems of the stream. Nederlo Creek would benefit from
the purchase of streambank easements from willing sellers and the restoration of in-stream
habitat. WDNR records indicate that Nederlo Creek was stocked with brown trout yearly from
1959 to 1995. Brook trout have been stocked since 1999. Access to Nederlo Creek is from
one road crossing and a WDNR easement.

From: 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

Nederlo Creek, Reads and Tainter Creeks Watershed (LW03) Fish and Aquatic Life

Nederlo Creek, Reads and Tainter Creeks Watershed (LW03) Recreation

Nederlo Creek, Reads and Tainter Creeks Watershed (LW03) Fish Consumption

General Condition

Water quality of Nederlo Creek was evaluated in 2020 and 2022; phosphorus and fish data indicate a healthy system. This stream segment is on the Healthy Waters List and is not considered impaired.

Date 2021

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

2020 Comprehensive WQ Assessments

2018 List of Healthy (Category 2) Waters

Comprehensive 2014 TP IBI Rivers Assessment

Crawford County Surface Water Resources 1972

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

Project Name (Click for Details)	Year Started
Fish Propagation Actions	2001

Monitoring Projects

WBIC	Official Waterbody Name	Station ID	Station Name	Earliest Fieldwork Date	Latest Fieldwork Date	View Station	View Data
1185700	Nederlo Creek	10013668	Nederlo Creek Station 2-Se 1/4 Nw 1/4 Sec. 12	1/1/2015	1/1/2015	Map	Data
1185700	Nederlo Creek	10013672	Nederlo Creek Section C-Sw 1/4 Ne 1/4 Sec. 12-Starts At Confluence Of N. Fork Nederlo(Creek 12-3)	1/1/2015	1/1/2015	Map	Data
1185700	Nederlo Creek	10013671	Nederlo Creek Section B-Se 1/4 Nw 1/4 Sec. 7-Starts At Freeman Rd. Bridge Crossing.	5/14/1997	1/1/2015	Map	Data
1185700	Nederlo Creek	119076	Nederlo Creek at Freeman Rd Bridge Site #120b	6/24/2003	10/23/2019	Map	Data
1185700	Nederlo Creek	10054176	Nederlo Creek 50 ft upstream of Unnamed Trib	5/22/2019	10/23/2019	Map	Data

Watershed Characteristics

Nederlo Creek is located in the Reads and Tainter Creeks watershed which is 135.69 mi². Land use in the watershed is primarily forest (47.20%), agricultural (24%) and a mix of grassland (23.30%) and other uses (5.50%). This watershed has 339.00 stream miles, 221.66 lake acres and 1,867.13 wetland acres.

Nonpoint Source Characteristics

This watershed is ranked High for runoff impacts on streams, Not Ranked 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

Nederlo Creek is considered a Cool-Cold Headwater 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.

Cool (Cold-Transition) Headwaters are small, usually perennial streams with cold to cool summer temperatures. Coldwater fishes are common to uncommon (<10 per 100 m), transitional fishes are abundant to common, and warm water fishes are uncommon to absent. Headwater species are abundant to common, mainstem species are common to absent, and river species are absent.

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