Hooper Area Pond IA 04-LDM-1084
Warren County S26T75NR24W 5 mi SSW of Indianola.
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: This lake is not designated for Class A1 (primary contact recreation) uses. 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 contaminant monitoring at this lake. 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.
EXPLANATION: Results from the ISU statewide survey of Iowa lakes and the UHL ambient lake monitoring program suggest that the high levels of algal turbidity may threaten full support of the Class B(LW) uses of Hooper Area Pond. Despite this potential threat, water transparency remains relatively good at this lake, and IDNR Fisheries feels that the Class B(LW) uses remain “fully supported.”
Using the median values from the ISU and UHL lake surveys from 2008-2012 (approximately 15 samples), Carlson’s (1977) trophic state indices for Secchi depth, chlorophyll a, and total phosphorus were 63, 66, and 64 respectively for Hooper Area Pond. According to Carlson (1977) the Secchi depth, chlorophyll a, and total phosphorus values all place Hooper Area Pond in between the eutrophic and the hypereutrophic categories. These values suggest high levels of chlorophyll a and suspended algae in the water, moderately poor water transparency, and moderately high levels of phosphorus in the water column.
The levels of inorganic suspended solids at this lake were relatively low and do not suggest an impairment due to non-algal turibidity. The median level of inorganic suspended solids in Hooper Area Pond (2.5 mg/L) and ranked 30th of the 134 lakes sampled by the ISU and UHL programs.
Data from the 2008-2012 ISU and UHL surveys suggest a moderate population of cyanobacteria exists at Hooper Area Pond, which does not contribute to an impairment due to nuisance aquatic life at this lake. These data show that cyanobacteria comprised only 35% of the phytoplankton wet mass at this lake. The median cyanobacteria wet mass (13.0 mg/L) and ranked 36th of the 134 lakes sampled.
The Class B(LW) (aquatic life) uses are assessed as “fully supported” based on information from IDNR’s Fisheries Bureau and results from the ISU and UHL lake surveys. The ISU and UHL lake surveys data from 2008-2012 show no violations of the Class B(LW) criteria for ammonia in 15 samples, pH in 15 samples, or dissolved oxygen in 15 samples.
Fish consumption uses remain "not assessed" due to the lack of fish contaminant monitoring in this lake.
Assessment Key Dates
| 8/21/2012 | Fixed Monitoring End Date |
| 5/5/2008 | 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 |