Iowa DNR
ADBNet

Water Quality Assessments

Impaired Waters List

Upper Iowa River IA 01-UIA-237

from Lane's Bridge (NW 1/4 S31 T100N R4W Allamakee Co.) to confluence with Canoe Cr. in S25 T99N R7W Winneshiek Co.

Assessment Cycle
2018
Release Status
Final
Data Collection Period
Overall IR Category
5 - Water is impaired or threatened and a TMDL is needed.
Trend
Unknown
Created
5/20/2019 8:40:47 AM
Updated
7/24/2019 8:42:50 AM
Assessment conducted in accordance with Iowa's 2018 IR methodology
Use Support
Class A1
Partially Supported
Bacteria: Indicator Bacteria- E. coli
Support Level
Partially Supported
Impairment Code
5a - Pollutant-caused impairment. TMDL needed.
Cause Magnitude
Slight
Status
Continuing
Source
Unknown: Source Unknown
Source Confidence
N/A
Cycle Added
2004
Impairment Rationale
Geometric mean criterion exceeded
Data Source
Ambient monitoring: Iowa DNR-rivers
TMDL Priority
Tier III
Class BWW1
Fully Supported
Class HH
Partially Supported
Fish Consumption Advisory: Mercury
Support Level
Partially Supported
Impairment Code
5a - Pollutant-caused impairment. TMDL needed.
Cause Magnitude
Slight
Status
Continuing
Source
Agriculture
Source Confidence
N/A
Cycle Added
2006
Impairment Rationale
Fish consumption advisory in effect: no more than 1 meal/week
Data Source
Fish contaminant monitoring: Iowa DNR
TMDL Priority
Tier IV
General Use
Not Assessed
Impairment Delistings
No delistings for this assessment cycle.
Documentation
Assessment Summary

The Class A1 (primary contact recreation) uses are assessed (monitored) as “partially supported” due to high levels of indicator bacteria that exceed state water quality criteria.  The Class B(WW1) aquatic life uses remain assessed (monitored) as "fully supported".  Fish consumption uses remain assessed (monitored) as “partially supported” based on high levels of mercury in fish samples and based on the resultant issuance and continuance of a fish consumption advisory for this segment of the Upper Iowa River.  Sources of data for this assessment include (1) results of DNR/SHL ambient monthly water quality monitoring conducted on the Upper Iowa River near Dorchester (station 10030001) during the period 2014 through 2016, (2) results of DNR/SHL biological monitoring in 2005, 2012, 2013, 2014 and 2016, and (3) results of U.S. EPA/DNR fish contaminant (RAFT) monitoring in 2004, 2006 and 2010. 

Assessment Explanation

The Class A1 (primary contact recreation) uses are assessed (monitored) as "partially supported" based on levels of indicator bacteria that exceeded state water quality criteria. The geometric means of indicator bacteria (E. coli) in the 24 samples collected during the recreational seasons of 2014 through 2016 at DNR station 10030001 on the Upper Iowa River near Dorchester were as follows: the 2014 geometric mean was 127 orgs/100 ml, the 2015 geometric mean was 64 orgs/100 ml, and the 2016 geometric mean was 125 orgs/100 ml. One of the three recreation season geometric means exceeded the Class A1 geometric mean criterion of 126 orgs/100 ml. Eight of the combined 24 samples (33 %) exceeded Iowa’s Class A1 single-sample maximum criterion of 235 orgs/100 ml. According to U.S. EPA guidelines for Section 305(b) reporting and Iowa DNR’s assessment/listing methodology, if the geometric mean is greater than 126 orgs/100 ml., the primary contact recreation uses should be assessed as "impaired" (see pgs 3-33 to 3-35 of U.S. EPA 1997b). Thus, because at least one recreation season geometric mean exceeded criteria for Class A1 uses, these uses are assessed as "partially supported."

Results of chemical/physical water quality monitoring at DNR station 10030001 on the Upper Iowa River near Dorchester suggest “full support” of the aquatic life uses. Monitoring showed no violations of Class B(WW1) water quality criteria for 36 Ammonia samples (maximum = 0.4 mg/L), 36 Dissolved Oxygen samples (minimum = 7.9 mg/L), 36 pH samples (range = 7.8 to 8.5), 36 Temperature samples (maximum = 23.6°C), 36 Chloride samples (maximum = 20 mg/L), or 36 Sulfate samples (maximum = 22 mg/L) occurred during monitoring from January 2014 to December 2016. According to U.S. EPA guidelines for Section 305(b) water quality assessments (U.S. EPA 1997b, page 3-17), the EPA guidelines allow up to 10% violations of these conventional parameters before impairment of water quality is indicated. Thus, these results thus suggest “full support” of the Class B(WW1) aquatic life uses.

Similarly, the Class B(WW1) aquatic life uses are assessed (evaluated) as “fully supporting" based on data collected in 2005, 2012, 2013, 2014 and 2016 as part of the DNR/SHL stream biocriteria and REMAP projects. A series of biological metrics that reflect stream water quality and habitat integrity were calculated from the biocriteria sampling data. The biological metrics are based on the numbers and types of benthic macroinvertebrate taxa and fish species collected in the stream sampling reach. The biological metrics were combined to make a fish community index of biotic integrity (FIBI) and a benthic macroinvertebrate index (BMIBI). The indexes rank the biological integrity of a stream sampling reach on a rising scale from 0 (minimum) to 100 (maximum). The 2005 REMAP FIBI scores were 57 (good) and 82 (excellent). The 2005, 2012, 2013, 2014 and 2016 BMIBI scores were 69, 70, 70, 72, 72 (all good) and 78, 81, 84 (all excellent). The aquatic life use support was assessed (evaluated) as fully supporting (=FS), based on a comparison of the FIBI and BMIBI scores with biological impairment criteria (BIC) established from a statistical analysis of data collected at stream ecoregion reference sites from 1994-2008. The FIBI BIC for this ecoregion is 52 and the BMIBI BIC for this ecoregion is 61. This segment passed the FIBI BIC 2/2 times in 2005 and passed the BMIBI BIC 8/8 times in the last five years. This assessment is considered evaluated because the drainage areas (768 and 897 mi2) above the sampling sites was greater than the maximum limit (500 mi2) that was used to calibrate the Iowa wadeable stream impairment criteria. Even though this site passed both the FIBI and BMIBI BICs, it is uncertain as to whether or not this segment is meeting the aquatic life criteria because the sites used for the assessment don't fall in the calibrated watershed size.


Fish consumption uses remain assessed (monitored) as “partially supported” based on results of U.S.EPA/DNR fish contaminant (RAFT) monitoring near Dorchester in 2004, 2006, and 2010. 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 composite samples of fillets from the 2004 samples of common carp and smallmouth bass had generally low levels of contaminants. Levels of primary contaminants in the composite sample of common carp fillets were as follows: mercury: 0.228 ppm; total PCBs: 0.13 ppm; and technical chlordane: <0.03 ppm. Levels of primary contaminants in the composite sample of smallmouth bass fillets were as follows: mercury: 0.486 ppm; total PCBs: 0.09 ppm; and technical chlordane: <0.03 ppm. The levels of mercury in 2004 samples of both common carp and smallmouth bass exceed the DNR/IDPH trigger level of 0.30 ppm for a one meal per week consumption advisory: the level of mercury in the sample of common carp fillets was 0.228 ppm and in the sample of smallmouth bass fillets was 0.486 ppm.

The composite samples of fillets from the 2006 RAFT samples of golden redhorse (Moxostoma erythrurum) and smallmouth bass had similarly high levels of mercury. The level of mercury in the composite sample of golden redhorse fillets was 0.362 ppm, and the level of mercury in the composite sample of smallmouth bass fillets was 0.37 ppm. According to the DNR/IDPH advisory protocol, if two consecutive samplings show that contaminant levels are above an advisory trigger level in fillet samples, a consumption advisory will be issued. Because levels of mercury in both the 2004 and 2006 samples of smallmouth bass exceed the DNR/IDPH trigger level of 0.30 ppm for a one meal per week consumption advisory, a consumption advisory was issued for this segment by DNR in March 2008. Because level of mercury in the sample of the bottom-feeding golden redhorse was also greater than the advisory level, all species were included in the one-meal/week advisory. The existence of a one-meal/week consumption advisory for this assessment segment suggests that the fish consumption uses are “partially supported.” This advisory extends from the Lower Dam in eastern Winneshiek County upriver to County Road W20 approximately 5.5 miles upriver from Decorah. Follow-up sampling was conducted at the Upper Iowa River near Dorchester in 2010. The level of mercury in samples of golden redhorse fillets (0.318 ppm) and smallmouth bass fillets (0.392 ppm) were both above the advisory trigger level therefore suggesting that the fish consumption advisory should remain at this river segment.

Monitoring and Methods
Assessment Key Dates
9/23/2004 Fish Tissue Monitoring
7/12/2006 Fish Tissue Monitoring
8/26/2010 Fish Tissue Monitoring
8/24/2005 Biological Monitoring
10/6/2005 Biological Monitoring
9/11/2012 Biological Monitoring
1/2/2014 Fixed Monitoring Start Date
12/7/2016 Fixed Monitoring End Date
9/11/2013 Biological Monitoring
10/8/2014 Biological Monitoring
8/16/2016 Biological Monitoring
Methods
220 Non-fixed station physical/chemical monitoring (conventional pollutant only)
230 Fixed station physical/chemical (conventional plus toxic pollutants)
260 Fish tissue analysis
315 Regional reference site approach
320 Benthic macroinvertebrate surveys
330 Fish surveys
380 Quantitative physical habitat assessment
420 Indicator bacteria monitoring