Iowa DNR
Iowa DNR
ADBNet
Water Quality Assessments
Impaired Waters List

Tuttle Lake (a.k.a. Okamanpeedan Lake) IA 04-EDM-975

Emmett County S14T100NR32W 2 mi. N of Dolliver.

Assessment Cycle
2014
Result Period
2010 - 2012
Designations
Class B(LW) Class A1 Class HH
Assessment Methodology
Assessment Type
Monitored
Integrated Report
Category 4a
Trophic
Hypereutrophic
Trend
Stable
Legacy ADBCode
IA 04-EDM-00290-L_0
Overall Use Support
Not supporting
Aquatic Life Use Support
Partial
Fish Consumption
Not assessed
Primary Contact Recreation
Not supporting
Documentation
Assessment Comments

Assessment is based on: (1) results of the statewide survey of Iowa lakes conducted from 2009-2012 by Iowa State University (ISU), (2) results of the statewide ambient lake monitoring program conducted in 2008 by University Hygienic Laboratory (UHL), and (3) information from the IDNR Fisheries Bureau.

Basis for Assessment

SUMMARY: The Class A1 (primary contact recreation) uses are assessed (monitored) as “not supported” due to very poor water transparency related to high levels of inorganic turbidity and algal blooms that violate Iowa’s narrative water quality standard protecting against aesthetically objectionable conditions.  The pH impairment at this lake is suggested for de-listing.  An additional impairment to these uses is suggested by the very large population of cyanobacteria at this lake.   The Class B(LW) aquatic life uses are assessed (monitored) as “fully supported.”  Fish consumption uses remain “not assessed” due to a lack of fish tissue data upon which to base an assessment.   Sources of data for this assessment include: (1) results of the statewide survey of Iowa lakes conducted from 2009-2012 by Iowa State University (ISU), (2) results of the statewide ambient lake monitoring program conducted in 2008 by University Hygienic Laboratory (UHL), and (3) information from the IDNR Fisheries Bureau.

Note:  A TMDL for algae and turbidity at Tuttle Lake was prepared by IDNR and approved by EPA in 2005, and these impairments for this lake were thus moved to IR Category 4a for the 2006 cycle.   This lake remains in Category 4a of the 2014 cycle.

EXPLANATION: Results from the ISU and UHL lake surveys suggest that the Class A1 uses at Tuttle Lake are “not supported.”  Using the median values from these surveys from 2008-2012 (approximately 14 samples), Carlson’s (1977) trophic state indices for Secchi depth, chlorophyll a, and total phosphorus were 77, 71,  and 75 respectively for Tuttle Lake.   According to Carlson (1977) the Secchi depth, chlorophyll a, and total phosphorus values all place Tuttle Lake in the hypereutrophic category.   These values suggest very high levels of chlorophyll a and suspended algae in the water, extremely poor water transparency, and extremely high levels of phosphorus in the water column.  

The level of inorganic suspended solids is extremely high at Tuttle Lake and suggests that non-algal turbidity contributes to the impairment.   The median inorganic suspended solids concentration at Tuttle Lake was 33.5 mg/L, and ranked highest of the 134 monitored lakes.

Data from the 2008-2012 ISU and UHL surveys suggest a very large population of cyanobacteria exists at Tuttle Lake, which contributes to an impairment due to nuisance aquatic life.   These data show that cyanobacteria comprised 87% of the phytoplankton wet mass at this lake.   The median cyanobacteria wet mass (85.9 mg/L) and ranekd 128th of the 134 lakes sampled.   This median is in the worst 25% of the 134 lakes sampled.   The presence of a large population of cyanobacteria at this lake suggests a potential violation of Iowa’s narrative water quality standard protecting against the occurrence of nuisance aquatic life.   This assessment is based strictly on the distribution of the lake-specific median cyanobacteria values from 2008-2012.   Median levels greater than the 75th percentile of this distribution were arbitrarily considered to represent potential impairment.   No other criteria exist, however, upon which to base a more accurate identification of impairments due to cyanobacteria.    The assessment category for assessments based on level of cyanobacteria will be considered "evaluated" (indicating an assessment with relatively lower confidence) as opposed to "monitored" (indicating an assessment with relatively higher confidence) to account for this lower level of confidence.

The Class B(LW) (aquatic life) uses are assessed (monitored) as “fully supported.”  The ISU and UHL lake surveys results show poor chemical water quality at Tuttle Lake due to excessive nutrient loading to the water column, organic enrichment, nuisance blooms of algae, and re-suspension of sediment.   Information from the IDNR Fisheries Bureau also suggests poor water quality at Tuttle Lake.   There were no violations for ammonia in 14 samples or for dissolved oxygen in 14 samples.   There were also no violations of the Class A1,B(LW) criterion for pH in 14 samples.   However, Tuttle Lake was assessed as “partially supporting” in the 2010 assessment/listing cycle due to significant violations of the pH criteria.   Based on IDNR’s assessment methodology 2 consecutive assessment/listing cycles without significantly greater than 10% of the samples violating the criterion are necessary to propose delisting based on pH violations.   Becasue there there no significant violations for pH in the 2012 or current 2014 assessment/listing cycles, the pH impairment is suggested for de-listing.  
  
Fish consumption uses remain "not assessed" due to the lack of fish contaminant monitoring in this lake.

Monitoring and Methods
Assessment Key Dates
8/29/2012 Fixed Monitoring End Date
5/21/2008 Fixed Monitoring Start Date
Methods
120 Surveys of fish and game biologists/other professionals
222 Non-fixed-station monitoring (conventional during key seasons and flows)
340 Primary producer surveys (phytoplankton/periphyton/macrophyton)
Monitoring Levels
Biological 3
Habitat 0
Physical Chemistry 3
Toxic 0
Pathogen Indicators 0
Other Health Indicators 0
Other Aquatic Life Indicators 0
# of Bio Sites 0
BioIntegrity N/A
Causes and Sources of Impairment
Causes Use Support Cause Magnitude Sources Source Magnitude
Suspended solids Primary Contact Recreation High
  • Agriculture
  • Sediment resuspension
  • Source Unknown
  • Moderate
  • High
  • Moderate
Noxious aquatic plants Primary Contact Recreation Moderate
  • Agriculture
  • Internal nutrient cycling (primarily lakes)
  • Source Unknown
  • Moderate
  • High
  • Moderate
Algal Grwth/Chlorophyll a Primary Contact Recreation High
  • Agriculture
  • Internal nutrient cycling (primarily lakes)
  • Source Unknown
  • Moderate
  • High
  • Moderate
Turbidity Primary Contact Recreation High
  • Agriculture
  • Sediment resuspension
  • Source Unknown
  • Moderate
  • High
  • Moderate