Iowa DNR
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Water Quality Assessments
Impaired Waters List

Big Creek Lake IA 04-UDM-1242

Polk County S22T81NR25W near Polk City

Assessment Cycle
2010
Result Period
2006 - 2008
Designations
Class A1 Class B(WW-1) Class HH
Assessment Methodology
Assessment Type
Monitored
Integrated Report
Category 5a
Trophic
Eutrophic
Trend
Stable
Legacy ADBCode
IA 04-UDM-0140-L_0
Overall Use Support
Not supporting
Aquatic Life Use Support
Fully
Fish Consumption
Fully
Primary Contact Recreation
Not supporting
Documentation
Assessment Comments

Assessment is based on: (1) results of the IDNR-UHL beach monitoring program in the summers of 2006, 2007, and 2008, (2) results of the statewide survey of Iowa lakes conducted from 2004 through 2007 by Iowa State University (ISU), (3) results of the statewide ambient lake monitoring program conducted from 2005 through 2008 by University Hygienic Laboratory (UHL), (4) information from the IDNR Fisheries Bureau, and (5) results of EPA/DNR fish contaminant (RAFT) monitoring in 2004.

Basis for Assessment

SUMMARY:  The Class A1 (primary contact recreation) uses are assessed (monitored) as “not supported” due to violations of the state water quality criteria for indicator bacteria.   The Class B(WW-1) (aquatic life) uses are assessed (monitored) as “fully supported” although information from the IDNR Fisheries Bureau suggests that algae blooms are a concern at this lake.   Fish consumption uses remain assessed (monitored) as “fully supported.”  Sources of data for this assessment include (1) results of the IDNR-UHL beach monitoring program in the summers of 2006, 2007, and 2008, (2) results of the statewide survey of Iowa lakes conducted from 2004 through 2007 by Iowa State University (ISU), (3) results of the statewide ambient lake monitoring program conducted from 2005 through 2008 by University Hygienic Laboratory (UHL), (4) information from the IDNR Fisheries Bureau, and (5) results of EPA/DNR fish contaminant (RAFT) monitoring in 2004.

EXPLANATION: Results of IDNR beach monitoring from 2006 through 2008 suggest that the Class A1 uses are "not supported."  Levels of indicator bacteria at Big Creek Lake beach were monitored once per week during the primary contact recreation seasons (May through September) of 2006 (28 samples), 2007 (16 samples), and 2008 (26 samples) as part of the IDNR beach monitoring program.   According to IDNR’s assessment methodology, all thirty-day geometric means for the three-year assessment period must be less than the state’s geometric mean criterion of 126 E.  coli orgs/100 ml for results of beach monitoring to indicate “full support” of the Class A1 (primary contact recreation) uses.   If a 5-sample, 30-day geometric mean exceeds the state criterion of 126 orgs/100 ml during the three-year assessment period, the Class A1 uses should be assessed as “not supported”.   This assessment approach is based on U.S.  EPA guidelines (see pgs 3-33 to 3-35 of U.S.  EPA 1997b).  

At Big Creek Lake beach, the geometric means of 5 thirty-day periods during the summer recreation season of 2008 exceeded the Iowa water quality standard of 126 E.  coli orgs/100 ml.   No geometric means violated this standard in 2006 or 2007.   The percentage of samples exceeding Iowa’s single-sample maximum criterion (235 E.  coli orgs/100 ml) was not significantly greater than 10% in any of the three years: 2006: 4%, 2007: 6%, 2008: 19%.  According to IDNR’s assessment methodology and U.S.  EPA guidelines, the violations of the geometric mean criterion suggest continued impairment (nonsupport) of the Class A1 (primary contact recreation) uses of Big Creek Lake.

Results from the ISU and UHL lake surveys, however, suggest full support of the Class A1 uses of Big Creek Lake.   Using the median values from these surveys from 2004 through 2008 (approximately 30 samples), Carlson’s (1977) trophic state indices for Secchi depth, chlorophyll a, and total phosphorus were 50, 55, and 61 respectively for Big Creek Lake.   According to Carlson (1977) the Secchi depth and chlorophyll a values places Big Creek Lake at the lower end of the eutrophic category.  The index value for total phosphorus places Big Creek Lake in between the eutrophic and hypereutrophic category.   These values suggest low levels of chlorophyll a and suspended algae in the water, very good water transparency, and moderately high levels of phosphorus in the water column.  

The level of inorganic suspended solids was low at this lake and does not suggest water quality problems due to non-algal turbidity.   The median level of inorganic suspended solids in Big Creek Lake (2.0 mg/L) was the 16th lowest median concentration among the 132 lakes sampled by the ISU and UHL lake surveys.

Data from the 2004-2008 ISU and UHL surveys suggest a small population of cyanobacteria exists at Big Creek Lake, which does not suggest an impairment at this lake.   These data show that cyanobacteria comprised 54% of the phytoplankton wet mass at this lake.   The median cyanobacteria wet mass (4.5 mg/L) was also the 26th lowest of the 132 lakes sampled.

The Class B(WW-1) (aquatic life) uses are assessed (monitored) as “fully supported” based on information from the IDNR Fisheries Bureau and results from the ISU and UHL lake surveys.   Information from the IDNR Fisheries Bureau suggests that algae blooms are getting worse and becoming a concern at this lake.   The ISU and UHL lake survey results show good chemical water quality at Big Creek Lake.   During 2004-2008 there were no violations of the Class B(WW-1) criterion for ammonia (29 samples), dissolved oxygen (30 samples), or pH (30 samples).  

Fish consumption uses were assessed (monitored) as “fully supported” based on results of U.S.  EPA/IDNR fish contaminant (RAFT) monitoring at Big Creek Lake in 2004.   The composite samples of fillets from channel catfish and largemouth bass had low levels of contaminants.   Levels of primary contaminants in the composite sample of channel catfish fillets were as follows: mercury: <0.0181 ppm; total PCBs: 0.09 ppm; and technical chlordane: <0.03 ppm.   Levels of primary contaminants in the composite sample of largemouth bass fillets were as follows: mercury: 0.043 ppm; total PCBs: 0.09 ppm; and technical chlordane: <0.03 ppm.   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 fish contaminant data generated from the 2004 RAFT sampling conducted at this lake show that 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
9/11/2008 Fixed Monitoring End Date
8/17/2004 Fish Tissue Monitoring
6/1/2004 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)
260 Fish tissue analysis
420 Water column surveys (e.g. fecal coliform)
Monitoring Levels
Biological 3
Habitat 0
Physical Chemistry 4
Toxic 0
Pathogen Indicators 4
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
Pathogens Primary Contact Recreation Moderate
  • Source Unknown
  • Moderate