Iowa DNR
Iowa DNR
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Water Quality Assessments
Impaired Waters List

Nine Eagles Lake IA 05-GRA-1361

Decatur County S18T67NR25W 3.5 mi. SE of Davis City.

Cycle
2018
Release Status
Final
Overall IR
5 - Water is impaired or threatened and a TMDL is needed.
Trophic
Mesotrophic
Trend
Improving
Created
10/16/2018 9:37:02 AM
Updated
6/6/2019 2:10:11 PM
Use Support
Class A1
Recreation - Primary contact
Partially Supported
Support Level
Partially Supported
Impairment Code
5a - Pollutant-caused impairment. TMDL needed.
Cause Magnitude
Moderate
Status
Continuing
Source
Unknown: Source Unknown
Source Confidence
N/A
Cycle Added
2006
Impairment Rationale
Geometric mean criterion exceeded
Data Source
Beach monitoring: Iowa DNR WQMA
TMDL Priority
Tier II
Class BLW
Aquatic Life - Lakes and wetlands
Fully Supported
Class C
Drinking Water -
Not Assessed
Class HH
Human Health -
Partially Supported
Support Level
Partially Supported
Impairment Code
5a - Pollutant-caused impairment. TMDL needed.
Cause Magnitude
High
Status
Continuing
Source
Agriculture
Source Confidence
N/A
Cycle Added
2006
Impairment Rationale
Fish consumption advisory in effect: no more than 1 meal/week
Data Source
Fish contaminant monitoring: Iowa DNR
TMDL Priority
Tier IV
General Use
General Use water -
Not Assessed
Impairment Delistings
No delistings for this assessment cycle.
Documentation
Assessment Summary

The Class A1 (primary contact recreation) uses are assessed (monitored) as “partially supported” (IR 5a) due to levels of indicator bacteria that exceed state water quality standards. The Class B(LW) (aquatic life) uses are assessed (monitored) as “fully supported” (IR 2a). Fish consumption uses remain assessed (monitored) as “partially supported” (IR 5a) due to the existence of a fish consumption advisory. The Class C (drinking water) uses remain “not assessed” (IR 3a) due to a lack of information upon which to base an assessment. Sources of data for this assessment include (1) results of IDNR/UHL beach monitoring from 2014 through 2016, (2) results of the statewide survey of Iowa lakes conducted from 2012 through 2016 by Iowa State University (ISU), (3) information from the IDNR Fisheries Bureau, and (4) results from the EPA/IDNR fish tissue monitoring program in 2007, 2009, and 2015.

Assessment Explanation

Results of DNR beach monitoring from 2014 through 2016 suggest that the Class A1 uses are "partially supported." Levels of indicator bacteria at Nine Eagles Beach were monitored once per week during the primary contact recreation seasons (May through September) of 2014 (32 samples), 2015 (16 samples) and 2016 (15 samples), as part of the DNR beach monitoring program. According to DNR’s assessment methodology two conditions need to be met for results of beach monitoring to indicate “full support” of the Class A1 (primary contact recreation) uses: (1) the geometric mean of the samples from each recreation season of the three-year assessment period are less than the state's geometric mean criterion of 126 E. coli orgs/100 ml and (2) not more than 10% of the samples during any one recreation season exceeds the state's single-sample maximum value of 235 E. coli orgs/100 ml. If a sampling season geometric mean exceeds the state criterion of 1000 orgs/100 ml during the three-year assessment period, the Class A1 uses should be assessed as “not supported.” Also, if a sampling season geometric mean exceeds the state criterion of 126 orgs/100 ml during the three-year assessment period and/or if significantly more than 10% of the samples in any one of the three recreation seasons exceed Iowa's single-sample maximum value of 235 E. coli orgs/100 ml, the Class A1 uses should be assessed as “partially supported.” This assessment approach is based on U.S. EPA guidelines (see pgs 3-33 to 3-35 of U.S. EPA 1997b).

At Nine Eagles Beach, the geometric means from 2014, 2015 and 2016 were all below the Iowa water quality standard of 126 E. coli orgs/100 ml. The geometric mean was 54 E. coli orgs/100 ml in 2014, 35 E. coli orgs/100 ml in 2015 and 63 E. coli orgs/100 ml in 2016. The percentage of samples exceeding Iowa's single-sample maximum criterion (235 E. coli orgs/100 ml) was 31% in 2014, 6% in 2015 and 27% in 2016. The number of samples exceeding the single-sample maximum criterion was significantly greater than 10% in 2014 and 2016. According to DNR's assessment methodology and U.S. EPA guidelines, these results suggest "partially supported" of the Class A1 uses.

For the 2018 assessment/listing cycle, the Class A1 (primary contact recreation) uses of Nine Eagles Lake are assessed (monitored) as "fully supported" based on information from the ISU lake survey. Using the median values from these surveys from 2012-2016 (approximately 15 samples), Carlson 's (1977) trophic state indices for Secchi depth, chlorophyll a, and total phosphorus were 47, 41, and 45 respectively for Nine Eagles Lake. According to Carlson (1977) the Secchi depth, chlorophyll a, and total phosphorus values all place Nine Eagles Lake in the Mesotrophic category. These values suggest extremely low levels of chlorophyll a and suspended algae in the water, exceptional water transparency, and extremely low levels of phosphorus in the water column. The data show no violations of the Class A1 criterion for pH in 15 samples.

Note: A TMDL for turbidity at Nine Eagles Lake was prepared by DNR and approved by EPA in 2001. Through the implementation of this TMDL, water clarity at this lake had improved such that the lake was de-listed for the 2004 assessment/listing cycle. Because, however, the 2006, 2008, 2010, 2012, 2014, 2016, and 2018 Section 303(d) impairments due to indicator bacteria and mercury in fish tissue at Nine Eagles Lake were not addressed in the TMDL, this waterbody remains in Category 5a (impaired; TMDL required) for the 2018 cycle.

The level of inorganic suspended solids was low at Nine Eagles Lake, and does not suggest water quality problems due to non-algal turbidity. The median level of inorganic suspended solids in Nine Eagles Lake (1.6 mg/L) was ranked 9th among the 138 lakes by the ISU lake survey.

Data from the 2012-2016 ISU lake survey suggest a small population of cyanobacteria exists at Nine Eagles Lake. These data show that cyanobacteria comprised 77% of the phytoplankton wet mass at this lake. The median cyanobacteria wet mass (3 mg/L) was ranked 27th of the 138 lakes sampled.

The Class B(LW) (aquatic life) uses are assessed (monitored) as "fully supported." Results of the ISU lake survey from 2012-2016 show there were no violations of the criterion for ammonia in 15 samples(0%), no violations of the criterion for dissolved oxygen in 15 samples(0%), and no violations of the criterion for pH in 15 samples(0%). Based on DNR's assessment methodology these violations are not significantly greater than 10% of the samples and therefore suggest (fully supported/monitored) of the Class B(LW) uses of Nine Eagles Lake.

The Class C (drinking water) uses are not assessed due to the lack of recent information upon which to base an assessment. The only parameter collected as part of the ISU lake surveys relevant to support of Class C (drinking water) uses is nitrate. While the results of the ISU surveys from 2012-2016 show that nitrate levels are extremely low at this lake (maximum value = 0.1 mg/l; median = 0 mg/l), these data are not sufficient for developing a valid assessment of support of the Class C uses.

Fish consumption uses remain assessed (monitored) as “partially supported” based on results of U.S.EPA/DNR fish contaminant (RAFT) monitoring at Nine Eagles Lake in 2007, 2009, and 2015. The existence of, or potential for, a fish consumption advisory is the basis for Section 305(b) assessments of the degree to which Iowa’s lakes and rivers support their fish consumption uses. Sampling conducted in 2007 and 2009 also showed that the levels of mercury in largemouth bass (0.412 ppm and 0.534 ppm, respectively) were above the one meal per week consumption advisory. Additionally, follow up sampling in 2015showed that the levels of mercury in largemouth bass (0.498 ppm) was also above the one meal per week consumption advisory.Therefore the consumption advisory remains at this lake and the fish consumption uses remain assessed as "partially supported."

Monitoring and Methods
Assessment Key Dates
5/21/2012
Fixed Monitoring Start Date
1/25/2001
TMDL Completed
7/30/2009
Fish Tissue Monitoring
10/1/2007
Fish Tissue Monitoring
8/30/2016
Fixed Monitoring End Date
7/8/2015
Fish Tissue Monitoring
Methods
120
Surveys of fish and game biologists/other professionals
222
Non-fixed-station monitoring (conventional during key seasons and flows)
260
Fish tissue analysis
340
Primary producer surveys (phytoplankton/periphyton/macrophyton)
420
Indicator bacteria monitoring