Iowa DNR
Iowa DNR
ADBNet
Water Quality Assessments
Impaired Waters List

Yellow Smoke Park Lake IA 06-BOY-1514

Crawford County S6T83NR38W 2 mi NE of Denison.

Cycle
2018
Release Status
Final
Overall IR
1 - All designated uses are met.
Trophic
Mesotrophic
Trend
Improving
Created
5/9/2019 8:59:40 AM
Updated
5/9/2019 9:05:52 AM
Use Support
Class A1
Recreation - Primary contact
Fully Supported
Class BLW
Aquatic Life - Lakes and wetlands
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 (primary contact recreation) uses are assessed (monitored) as “fully supported” (IR 2a). The Class B(LW) aquatic life uses are also assessed (monitored) as “fully supported” (IR 2a). Information from the Iowa DNR Fisheries Bureau indicates that the previous impairment due to siltation has been addressed and removed. The fish consumption (Class HH) uses are assessed (monitored) as "fully supported" (IR 2a). Sources of data for this assessment include (1) results of the statewide survey of Iowa lakes conducted from 2012 through 2016 by Iowa State University (ISU); (2) information from the IDNR Fisheries Bureau; (3) results of U.S. EPA/IDNR turtle contaminant monitoring in 2009 and fish tissue monitoring in 2011, 2012, and 2014; and (4) information from the Iowa DNR fisheries management biologist (B. Wallace) at Yellow Smoke Lake.

Assessment Explanation

For the 2018 assessment/listing cycle, the Class A1 (primary contact recreation) uses of Yellow Smoke Park 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 46, 51, and 49 respectively for Yellow Smoke Park Lake. According to Carlson (1977) the Secchi depth, chlorophyll a, and total phosphorus values all place Yellow Smoke Park Lake in between the Mesotrophic and the Eutrophic categories. These values suggest 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.

The level of inorganic suspended solids was low at Yellow Smoke Park Lake, and does not suggest water quality problems due to non-algal turbidity. The median level of inorganic suspended solids in Yellow Smoke Park 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 Yellow Smoke Park Lake. These data show that cyanobacteria comprised 32% of the phytoplankton wet mass at this lake. The median cyanobacteria wet mass (2.6 mg/L) was ranked 22nd 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 Yellow Smoke Park Lake.

Information from the DNR Fisheries Bureau indicates that the previous impairment due to siltation in the upper arm of this lake was addressed and corrected. According to DNR Fisheries, over the last 10 years, the Crawford County Conservation Board was awarded a fish habitat grant to rectify the siltation problem at Yellow Smoke Lake. As a result, silt was removed from the upper end of the lake via backhoe, the shoreline was armored in the upper end, a partial sediment trap/basin was installed in the very upper end of the lake, and an additional sediment pond was constructed on private property further up in the lake’s watershed.Also, pea gravel/sand bed was placed in the north arm of the lake to create bluegill spawning habitat. A 2010 fish survey shows that the fish populations at this lake are well balanced, healthy and that natural reproduction is occurring on a consistent basis.

The fish consumption (Class HH) uses are assessed (monitored) as "fully supported" (IR 2a). Monitoring conducted in 2012 on largemouth bass.The average level of mercury in the tissue plug samples from five largemouth bass was 0.218 ppm (SD=0.074 ppm; maximum=0.331 ppm) and was below Iowa's advisory threshold of 0.3 ppm. The average level of mercury in the next (2014) sample of five largemouth bass from Yellow Smoke was 0.194 ppm (SD=0.093 ppm; Max.= 0.29 ppm). Similar to the results from the 2012 sampling, the 2014 average level of mercury was below the consumption advisory threshold of 0.3 ppm.

U.S.EPA/DNR contaminant (RAFT) monitoring at Yellow Smoke Lake in 2009 showed that levels of contaminant in turtle tissue were below Iowa's consumption advisory thresholds.The composite samples of shoulder tissue from snapping turtle had low levels of contaminants.Levels of primary contaminants in the shoulder tissue of snapping turtle were as follows: mercury: 0.122 ppm; total PCBs: 0.09 ppm; and technical chlordane: <0.03 ppm. Thus, the turtle contaminant data generated from the 2009 RAFT sampling show that the levels of contaminants do not exceed any of Iowa's advisory thresholds for a one-meal/week advisory (0.3 ppm for mercury, 0.2 ppm for PCBs, and 0.6 ppm for chlordane).

Note: A TMDL for siltation at Yellow Smoke Lake was prepared by DNR and approved by EPA in 2002.

Monitoring and Methods
Assessment Key Dates
5/14/2012
Fixed Monitoring Start Date
8/16/2016
Fixed Monitoring End Date
8/28/2009
Fish Tissue Monitoring
9/29/2011
Fish Tissue Monitoring
9/24/2012
Fish Tissue Monitoring
8/4/2014
Fish Tissue Monitoring
5/27/2010
Biological Monitoring
7/29/2010
Biological Monitoring
1/28/2002
TMDL Completed
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)