Iowa DNR
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Water Quality Assessments
Impaired Waters List

Briggs Woods Lake IA 04-UDM-1255

Hamilton County S17T88NR25W near Webster City.

Assessment Cycle
2004
Result Period
2000 - 2002
Designations
Assessment Methodology
Assessment Type
Evaluated
Integrated Report
Category 1
Trophic
Eutrophic
Trend
Stable
Legacy ADBCode
IA 04-UDM-01880-L_0
Overall Use Support
Threatened
Aquatic Life Use Support
Threatened
Fish Consumption
Fully
Primary Contact Recreation
Threatened
Documentation
Assessment Comments

Assessment is based on results of (1) ISU lake survey from 2000-02, (2) surveys by IDNR Fisheries Bureau, (3) ISU report on lake plankton communities in 2000, and (4) results of U.S. EPA/IDNR fish tissue (RAFT) monitoring in 1994.

Basis for Assessment

SUMMARY:  The Class A (primary contact recreation) uses are assessed (evaluated) as "fully supporting / threatened" due to the presence of nuisance (=noxious) aquatic (algal) life (bluegreen algae).   The Class B(LW) aquatic life uses are assessed (evaluated) as "fully supporting / threatened" due to nutrient loading to the water column.   Fish consumption uses are assessed (evaluated) as "fully supported" based on results of fish contaminant monitoring in 1994.   The sources of data for this assessment include (1) results of the statewide survey of Iowa lakes conducted from 2000 through 2002 by Iowa State University (ISU), (2) information from the IDNR Fisheries Bureau, (3) information on plankton communities at Iowa lakes in 2000 from Downing et al.  (2002), and (4) results of IDNR/U.S.  EPA fish tissue monitoring in 1994.  

EXPLANATION:  Using the median values from this survey from 2000 through 2002 (approximately nine samples), Carlson's (1977) trophic state indices for total phosphorus, chlorophyll-a, and secchi depth are 66, 53, and 50, respectively.   According to Carlson (1977), the index value for total phosphorus places this lake in the middle range between eutrophic and hyper-eutrophic lakes; the index values for chlorophyll-a and Secchi depth, however, place this lake in the lower range of eutrophic lakes.   These index values suggest (1) moderately high levels of phosphorus, (2) low (and less than expected) production of suspended algae, and (3) very good (and better than expected) water transparency.   According to Carlson (1991), the occurrence of a high TSI value for total phosphorus with relatively low values for chlorophyll-a and secchi depth indicates that some factor (e.g., nitrogen limitation, zooplankton grazing, or some other factor) other than phosphorus limits production of algae.   The ISU lake data suggest that algal production at Briggs Woods Lake may be limited by zooplankton grazing.   Data from Downing et al.  (2002) show that the zooplankton community of this lake has a moderately large population (approximately 40% dry mass) of species known as algal grazers; the median summer mass of zooplankton grazers at this lake in 2000 (18 mg/l) was the 69th highest of the 131 lakes sampled.   Neither nitrogen availability nor inorganic turbidity, however, appear to limit algal production.   Based on median values from ISU sampling from 2000-02, the ratio of total nitrogen to total phosphorus for Briggs Woods Lake is 187; this extremely high ratio reflects the extremely high concentration of total nitrogen at this lake:  the 2000-02 summer median total nitrogen at this lake (13.4 mg/l) was the second highest of the 131 lakes sampled.   The levels of inorganic suspended solids at this lake are very low and do not suggest the potential for impairing designated uses.   The median level of inorganic suspended solids in the 131 lakes sampled for the ISU lake survey from 2000 through 2002 was 4.8 mg/l; the median level at Briggs Woods Lake was 2.2 mg/l; this was the 13th lowest level of the 131 lakes sampled.

Data from Downing et al.  (2002) suggest that bluegreen algae (Cyanophyta) dominate the summertime phytoplankton community of this lake (greater than 75% on a wet mass basis).   The average mass of bluegreen algae in summer 2000 at this lake (22 mg/l) ranked 41st highest of the 131 lakes sampled.   The presence of a moderately large population of bluegreen algae suggests a threat to support of the designated uses of this lake due to the potential for violating Iowa’s narrative water quality standard protecting against presence of nuisance aquatic life.   Although results of plankton sampling in 2000 suggest that designated uses are threatened by nuisance aquatic (e.g., algal) life, the amount of data available for characterizing algal populations at this lake (one season) is not sufficient for developing a more accurate assessment of support of these uses.   Thus, the assessment category is considered "evaluated" (indicating an assessment with relatively lower confidence) as opposed to "monitored" (indicating an assessment with relatively higher confidence).   Additional data on plankton have been collected at this lake as part of the ongoing ISU lake survey and will be used to improve the accuracy of future water quality assessments.  

The eutrophic conditions at this lake, along with information from the IDNR Fisheries Bureau, suggest that the Class B(LW) aquatic life uses should be assessed as "fully supported / threatened" due to nutrient loading to the water column.   Fish consumption uses remain assessed (evaluated) as "fully supported" based on results of the U.S.  EPA/IDNR fish tissue (RAFT) monitoring in 1994 (see assessment developed for the 1996 report).   However, because these data are now considered too old (greater than five years) to accurately characterize current water quality conditions, the assessment category is changed from "monitored" (indicating an assessment with relatively high confidence) to "evaluated" (indicating an assessment with relatively low confidence).

Monitoring and Methods
Assessment Key Dates
8/12/2002 Fixed Monitoring End Date
7/10/2000 Fixed Monitoring Start Date
9/1/1994 Fish Tissue Monitoring
Methods
340 Primary producer surveys (phytoplankton/periphyton/macrophyton)
120 Surveys of fish and game biologists/other professionals
222 Non-fixed-station monitoring (conventional during key seasons and flows)
260 Fish tissue analysis
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
Noxious aquatic plants Primary Contact Recreation Not Impairing
  • Internal nutrient cycling (primarily lakes)
  • Not Impairing
Nutrients Aquatic Life Support Not Impairing
  • Agriculture
  • Natural Sources
  • Not Impairing
  • Not Impairing