Iowa DNR
Iowa DNR
ADBNet
Water Quality Assessments
Impaired Waters List

Saylorville Reservoir IA 04-UDM-1213

Polk County Saylorville Dam to Polk-Dallas county line.

Cycle
2020
Release Status
Final
Overall IR
5 - Water is impaired or threatened and a TMDL is needed.
Trophic
Eutrophic
Trend
Stable
Created
8/14/2020 1:45:59 PM
Updated
10/14/2020 1:17:05 PM
Use Support
Class A1
Recreation - Primary contact
Not Supported
Support Level
Not Supported
Impairment Code
5a - Pollutant-caused impairment. TMDL needed.
Cause Magnitude
Moderate
Status
Continuing
Source
Other: Sediment Resuspension
Source Confidence
Moderate
Cycle Added
2016
Impairment Rationale
Narrative criteria violation: aesthetically objectionable conditions
Data Source
Ambient monitoring: Corps of Engineers/ISU/UI
TMDL Priority
Tier II
Support Level
Not Supported
Impairment Code
5a - Pollutant-caused impairment. TMDL needed.
Cause Magnitude
Moderate
Status
New
Source
Unknown: Source Unknown
Source Confidence
N/A
Cycle Added
2020
Impairment Rationale
Geometric mean criterion exceeded
Data Source
Ambient monitoring: Corps of Engineers/Iowa DNR-Lakes
TMDL Priority
Tier II
Class BWW1
Aquatic Life - Warm Water Type 1
Fully Supported
Class HH
Human Health -
Fully Supported
General Use
General Use water -
Not Assessed
Impairment Delistings
No delistings for this assessment cycle.
Documentation
Assessment Summary

The Class A1 use of Saylorville Reservoir is assessed (monitored) as "not supported” due to poor water transparency caused by non-algal turbidity and due to high levels of indicator bacteria. The Class BWW1 use is assessed (monitored) as "fully supported." Class HH use remains assessed (monitored) as "fully supported" based on ACOE-sponsored annual fish contaminant monitoring from 2012-14.

Assessment Explanation

Sources of Data:

Data Source

Data Source ID

Data Type

Data Age

Site ID

Site Name

Site Description

USACE

12

WQ

CY 2014-2018

27770001

Saylorvill Reservoir - Surface

Lake Deep point

USACE

12

WQ

CY 2016-2018

99990030

Oak Grove Beach Saylorville

USACE

12

WQ

CY 2016-2018

99990031

Sandpiper Beach Saylorville

USACE

FT

See Below

Saylorvill Reservoir

Iowa DNR

6

WQ

CY 2014-2016

22770005

Saylorville Reservoir

Lake Deep point


Class A1 - Indicator Bacteria:

Site ID

Data Source ID

# Samples / # Years

2016 Geometric Mean

2017 Geometric Mean

2018 Geometric Mean

Annual Geometric Mean Violation

# Violations

% Violations

Significantly >10% Violations

Assessment Type

Support Level

27770001

12

54 / 4

1.88

NA

NA

No

0

0%

NO

Monitored

Full

99990030

12

35 / 3

12.5

18.95

410.6

Yes

3

9%

YES

Monitored

Partial

99990031

12

44 / 3

17.04

15.05

26.65

No

3

7%

NO

Monitored

Full


Class A1 - pH:

Site ID

Data Source ID

# Samples / # Years

Maximum Value

Mean Value

Median Value

# Violations

% Violations

Significantly >10% Violations

Assessment Type

Support Level

22770005

6

9 / 3

8.51

8.06

8

0

0%

NO

Evaluated

Full

27770001

12

82 / 5

8.68

8.15

8.18

0

0%

NO

Monitored

Full


Class A1 - Lake TSI's

Site ID

Data Source ID

Parameter Name

# Samples / # Years

Minimum Value

Maximum Value

Median Value

Median TSI Violation

Assessment Type

Support Level

22770005

6

Chlorophyll a TSI

9 / 3

41

67

59

NO

Monitored

Full

27770001

12

Chlorophyll a TSI

51 / 5

31

77

61

NO

Monitored

Full

22770005

6

Secchi TSI

9 / 3

54

73

67

YES

Monitored

Not

27770001

12

Secchi TSI

82 / 5

41

79

67

YES

Monitored

Not

22770005

6

Total Phosphorus TSI

9 / 3

63

82

72

NA

NA

NA

27770001

12

Total Phosphorus TSI

82 / 5

49

108

75

NA

NA

NA

22770005

6

Inorganic suspended solids

9 / 3

1.05

18.6

8.6

NA

NA

NA


Class BWW1 - 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

22770005

6

Ammonia

9 / 3

0.306

0.08

0.05

0 / 0

0% / 0%

NO

Evaluated

Full

27770001

12

Ammonia

82 / 5

1.12

0.12

0.06

0 / 0

0% / 0%

NO

Monitored

Full

22770005

6

Dissolved oxygen

9 / 3

16.42

9.07

6.75

NA / 0

NA / 0%

NO

Evaluated

Full

27770001

12

Dissolved oxygen

82 / 5

19.11

9.37

9.14

NA / 2

NA / 2%

NO

Monitored

Full

22770005

6

pH

9 / 3

8.51

8.06

8

0 / NA

0% / NA

NO

Evaluated

Full

27770001

12

pH

82 / 5

8.68

8.15

8.18

0 / NA

0% / NA

NO

Monitored

Full

22770005

6

Temperature

9 / 3

25.81

22.02

22.49

0 / 0

0% / 0%

NO

Evaluated

Full

27770001

12

Temperature

82 / 5

29.2

19.6

22.2

0 / 0

0% / 0%

NO

Monitored

Full


Class BLW - Lake Planktonic Cyanobacteria:

Site ID

Data Source ID

# Samples

Maximum Cyanobacteria Wet Mass

Maximum Cyanobacteria % Composition

Median Cyanobacteria Wet Mass

Median Cyanobacteria % Composition

Median Cyanobacteria Wet Mass = 75th Percentile

Assessment Type

Support Level

22770005

6

9

26.917

92.3 %

8.169

50 %

NO

Evaluated

NA


Class HH - Fish Tissue Sampling:

Fish consumption uses were assessed (monitored) as “fully supported” based on results of ACOE/ISU fish contaminant monitoring at Saylorville Reservoir in 2012-2014. The composite samples of whole-fish common carp had low levels of contaminants. Levels of total chlordane in the composite samples were as follows: 2012: 0.002ppm; 2013: 0.004ppm; 2014: 0.130ppm. None of these levels approach the advisory trigger level of 0.6ppm for chlordane. In 2012, 2013, and 2014, composite samples of whole-fish carp were analyzed for total PCBs and Aroclors 1248, 1254, and 1260. Total PCBs in composite samples of whole-fish carp were 0.002 ppm (2012) and 0.002 (2013).PCB Aroclors 1248, 1254, and 1260 were all 0.0002 ppm(2014).The levels of PCBs seen in fish tissue samples from ISU/ACOE in Saylorville Reservoir are well below the one meal per week advisory trigger of 0.20 ppm for total PCBs. 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. The levels of contaminants do not exceed any of the advisory trigger levels, thus indicating no justification for issuance of a consumption advisory for this waterbody.

Monitoring and Methods
Assessment Key Dates
4/7/2014
Fixed Monitoring Start Date
11/5/2018
Fixed Monitoring End Date
5/15/2012
Fish Tissue Monitoring
7/31/2013
Fish Tissue Monitoring
5/28/2014
Fish Tissue Monitoring
Methods
120
Surveys of fish and game biologists/other professionals
222
Non-fixed-station monitoring (conventional during key seasons and flows)
230
Fixed station physical/chemical (conventional plus toxic pollutants)
260
Fish tissue analysis
340
Primary producer surveys (phytoplankton/periphyton/macrophyton)
420
Indicator bacteria monitoring