Iowa DNR
Iowa DNR
ADBNet
Water Quality Assessments
Impaired Waters List

Big Marsh IA 02-WFC-803

Butler County S25T91NR17W 5 mi N of Parkersburg.

Cycle
2020
Release Status
Final
Overall IR
3 - Insufficient data exist to determine whether any designated uses are met.
Trend
Unknown
Created
7/29/2020 8:06:15 AM
Updated
10/13/2020 1:22:06 PM
Use Support
Class BLW
Aquatic Life - Lakes and wetlands
WINOFI
Impairment Code
3b - Use potentially impaired based on an evaluated assessment.
Cause Magnitude
Slight
Status
Continuing
Source
Hydromodification: Bank or Shoreline Modification or Destabilization
Source Confidence
Low
Cycle Added
1994
Impairment Rationale
Adverse impacts on plant/animal communities
Data Source
Biological monitoring: Iowa DNR Wildlife
Impairment Code
3b - Use potentially impaired based on an evaluated assessment.
Cause Magnitude
Slight
Status
Continuing
Source
Agriculture
Source Confidence
Low
Cycle Added
1994
Impairment Rationale
Adverse impacts on plant/animal communities
Data Source
Biological monitoring: Iowa DNR Wildlife
Class HH
Human Health -
Not Assessed
General Use
General Use water -
Not Assessed
Impairment Delistings
No delistings for this assessment cycle.
Documentation
Assessment Summary

The Class BLW use remains assessed as "partially supported" based on information from the IDNR Wildlife Bureau. All other designated uses are “not assessed”.

Assessment Explanation

Sources of Data:

Data Source

Data Source ID

Data Type

Data Age

Site ID

Site Name

Site Description

Iowa DNR

6

WQ

CY 2014-2017

23000041

Wetland 61


Class BLW - TSI's

Site ID

Data Source ID

Parameter Name

# Samples / # Years

Minimum Value

Maximum Value

Median Value

Median TSI Violation

Assessment Type

Support Level

23000041

6

Chlorophyll a TSI

6 / 3

24

83

46

NO

Evaluated

Full

23000041

6

Inorganic suspended solids

4 / 2

1

1429

10

NA

NA

NA

  • The TSI value for Secchi depth is not used to evaluate the attainment of aquatic life goals in shallow lakes. Due to the depth of these shallow lakes, TSI values for Secchi depth can be misleading. In some instances, the Secchi disk remains visible at the bottom of the lake and the depth of the lake is recorded as the Secchi depth. In these instances, water clarity may be sufficient to support the Class B(LW) uses, but the index value is limited by the depth of the lake. Thus the combination of total suspended solids and chlorophyll a will be used to determine whether or not the Class B(LW) uses are impaired in these shallow systems.

Class BLW - Conventional Parameters:

Site ID

Data Source ID

Parameter Name

# Samples / # Years

Maximum Value

Mean Value

Median Value

# Acute / Chronic Violations

% Acute/ Chronic Violations

Significantly >10% Violations

Assessment Type

Support Level

23000041

6

Ammonia

5 / 3

2.8526

0.72

0.08

0 / 1

0% / 20%

NO

Evaluated

Full

23000041

6

Dissolved oxygen

6 / 3

10.65

7.12

8.02

NA / 1

NA / 17%

NO

Evaluated

Full

23000041

6

pH

5 / 3

8.66

8.03

7.83

0 / NA

0% / NA

NO

Evaluated

Full

23000041

6

Temperature

6 / 3

30

23

22

0 / 0

0% / 0%

NO

Evaluated

Full


Class BLW - Protection of Submerged Aquatic Vegetation:

Site ID

Data Source ID

Parameter Name

# Samples / # Years

Minimum Value

Maximum Value

Median Value

Median Value >= SAV

Assessment Type

Support Level

23000041

6

Total suspended solids

6 / 3

13

1810

35

Yes

Evaluated

Full

  • Guidelines for wetland assessment from the Upper Mississippi River Conservation Committee’s Water Quality Technical Section (2003) state that an average total suspended solids concentration during the growing season of less than 30 mg/L is necessary to provide sufficient water clarity to support the growth of submersed aquatic vegetation in wetlands and shallow lakes. High levels of total suspended solids impede the growth of submersed aquatic vegetation (SAV). Submersed aquatic vegetation is critical to the health of wetland and shallow lake ecosystems. The elimination of SAV can degrade habitat quality such that undesirable aquatic species such as cyanobacteria, common carp and fathead minnows dominate. As such, the suppression of SAV constitutes a violation of Iowa’s narrative water quality criteria protecting against undesirable or nuisance aquatic life.

Class BLW - Toxic Parameters:

Site ID

Data Source ID

Parameter Name

# Samples / # Years

Maximum Value

Mean Value

Median Value

# Acute / Chronic Violations

% Acute/ Chronic Violations

>1 Acute / Chronic Violation

Assessment Type

Support Level

23000041

6

Parathion

1 / 1

0.05

0.05

0.05

0 / 0

0% / 0%

NO

Evaluated

Full

23000041

6

Pentachlorophenol

3 / 3

0.1

0.1

0.1

0 / 0

0% / 0%

NO

Evaluated

Full


Class HH-F - Toxic Parameters:

Site ID

Data Source ID

Parameter Name

# Samples / # Years

Maximum Value

Mean Value

Median Value

Number of Non - Detects

Mean Value > Criterion or MCL

Assessment Type

Support Level

23000041

6

Pentachlorophenol

3 / 3

0.1

0.1

0.1

3

NO

Evaluated

Full


Note: The aquatic life uses remain assessed as "partially supported" based on information from the Iowa DNR Wildlife Bureau (see assessment for the 1998 and 2000 assessment cycles). The assessment category for this wetland of "evaluated" indicates that the assessment is based entirely on "best professional judgment."In terms of Section 305(b) reporting, "monitored assessments" are based primarily on recent, site-specific ambient monitoring data and thus have relatively high confidence. DNR considers waterbodies identified as "impaired" based on "monitored assessments" as candidates for the state's Section 303(d) list. "Evaluated assessments" are those based on data older than five years or other than site-specific ambient monitoring data (e.g., questionnaire surveys of fish and game biologists [=best professional judgment]) and thus have relatively lower confidence. DNR does not consider waterbodies identified as "impaired" based on "evaluated assessments" as candidates for the state's Section 303(d) list.

Monitoring and Methods
Assessment Key Dates
5/22/2014
Fixed Monitoring Start Date
7/6/2017
Fixed Monitoring End Date
Methods
120
Surveys of fish and game biologists/other professionals