Iowa DNR
Iowa DNR
ADBNet
Water Quality Assessments
Impaired Waters List

Milford Creek IA 06-LSR-1666

mouth (S14 T98N R37W Dickinson Co.) to confluence with unnamed tributary in S18 T98N R36W Dickinson Co.

Cycle
2020
Release Status
Final
Overall IR
4 - Water is impaired or threatened and a TMDL has been completed or is not needed.
Trend
Unknown
Created
9/22/2020 12:47:54 PM
Updated
10/16/2020 3:16:33 PM
Use Support
Class A3
Recreation - Children's contact
Not Assessed
Class BWW2
Aquatic Life - Warm Water Type 2
Partially Supported
Support Level
Partially Supported
Impairment Code
4a - Pollutant-caused impairment. TMDL has been completed.
Cause Magnitude
Moderate
Status
Continuing
Source
Multiple Sources
Source Confidence
Moderate
Cycle Added
2008
Impairment Rationale
Low Biotic Index
Data Source
Biological monitoring: Iowa DNR WQMA
Support Level
Partially Supported
Impairment Code
4a - Pollutant-caused impairment. TMDL has been completed.
Cause Magnitude
Moderate
Status
Continuing
Source
Multiple Sources
Source Confidence
Low
Cycle Added
2008
Impairment Rationale
Low Biotic Index
Data Source
Biological monitoring: Iowa DNR WQMA
Support Level
Partially Supported
Impairment Code
4a - Pollutant-caused impairment. TMDL has been completed.
Cause Magnitude
Moderate
Status
Continuing
Source
Municipal Wastewater: Municipal Point Sources
Source Confidence
High
Cycle Added
2008
Impairment Rationale
Low Biotic Index
Data Source
Biological monitoring: Iowa DNR WQMA
Class HH
Human Health -
Not Assessed
General Use
General Use water -
Not Assessed
Impairment Delistings
No delistings for this assessment cycle.
Documentation
Assessment Summary

The Class BWW2 aquatic life use remains assessed as "partially supported" based on 2001 and 2005 biological sampling data. All other designated uses were "not assessed". Note: A TMDL for phosphorus was approved by EPA in December 2008. As noted in the TMDL, DNR’s 2004 stressor identification document for Milford Creek identified excessive aquatic vegetation (both algae and macrophytes) and low levels of dissolved oxygen as the primary stressors of the fish and aquatic macroinvertebrate communities of this stream segment. The high level of phosphorus in this stream, as documented as part of previous Section 305(b) assessments and as part of the 2008 TMDL, was identified as the causal factor behind the responses of excessive vegetation and low levels of dissolved oxygen. Because the 2008 TMDL covers these causal factors, the biological impairment identified for the 2004 and 2006 listing cycles was moved from IR Category 5b to Category 4a (impaired; TMDL approved).

Assessment Explanation

Sources of Data:

Data Source

Data Source ID

Data Type

Data Age

Site ID

Site Name

Site Description

Iowa DNR

6

BIO

See Below

244

Milford Creek

Milford – DS TMDL

Iowa DNR

6

WQ

See Below

11300002

Milford Creek

Site 49

Iowa DNR

6

WQ

See Below

11300015

Milford Creek

At 225 Ave (Site 2)

Class BWW2 - Biological Sampling:

Benthic Macroinvertebrates:

BioNet Site ID

Date

Drainage Area (mi2)

Ecoregion

Major Drainage/ Thermal

BM Sample Gear

BMIBI score

BMIBI Class

47b BMIBI BIT

BMIBI Pass/ Fail

244

9/14/05

136

47b

MO/WW

Hess

13

Poor

62

Fail

244

9/5/01

136

47b

MO/WW

Hess

43

Fair

62

Fail

Overall:

Community

Assessment Type

Assessment Result

Support Level

Earned IR Category

Actual IR Category

Reason

Benthic Macroinvertebrates

Evaluated

Fail (0/2)

Partial

3bc

4a

Assessment is evaluated because it was based on samples not collected in the last five years.


Class BWW2 - Conventional Parameters:

Results of chemical monitoring conducted in this segment as part of TMDL-related monitoring during the period from May 2004 to September 2005 suggest water quality problems in this stream reach but do not suggest impairment of the Class BWW2 aquatic life use. Two of 20 samples (10%) violated the Class BWW2 criterion for dissolved oxygen of 5 mg/l; these samples were collected on August 4 (3.9 mg/l) and August 10 (4.2 mg/l) of 2004. One of 17 samples (6%) violated the Class BWW2 criterion for pH. The pH of the sample collected on June 7, 2004 was 9.3 units, thus exceeding the criterion of 9.0 pH units.Two of 14 samples collected from 2004-2005 violated the Class B(WW2) chronic criteria for ammonia; these samples were collected on July 6, 2004 (4.5 mg/l) and July 12, 2004 (0.74 mg/l).Based on DNR’s assessment methodology, however, these results do not suggest that the violation frequency for dissolved oxygen, pH or ammonia is significantly greater than 10% and thus do not suggest impairment of the Class BWW2 use of this segment of Milford Creek.

Limited monitoring at TMDL Site 2 (Station 11300015; 1 mile SSE of Milford) from July to September 2005 did not show violations of Class BWW2 criteria; no violations occurred for ammonia (maximum = 0.21 mg/l), pH (range of 7.9-8.4), or dissolved oxygen (minimum = 6.8 mg/l) in the four samples collected during this period. Although these results suggested good water quality, the number of samples and period of time covered was limited and does not provide for development of a higher confidence (monitored) assessment.

This stream has historically shown elevated levels of phosphorus. The mean, median, and maximum total phosphorus levels for the 24 sampling events from May 2004 through September 2005 at TMDL monitoring station 49 in lower Milford Creek were 1.4, 1.5, and 3.0 mg/l, respectively. Summary statistics for dissolved phosphorus, measured as orthophosphate, for these 24 sampling events (mean, median, and maximum) were 1.2, 1.3, and 3.1 mg/l, respectively.

Monitoring and Methods
Assessment Key Dates
3/13/2001
Fixed Monitoring Start Date
11/13/2001
Fixed Monitoring End Date
5/29/2004
Fixed Monitoring Start Date
10/11/2004
Fixed Monitoring End Date
9/5/2001
Biological Monitoring
9/14/2005
Biological Monitoring
12/11/2008
TMDL Completed
Methods
150
Monitoring data more than 5 years old
220
Non-fixed station physical/chemical monitoring (conventional pollutant only)
315
Regional reference site approach
320
Benthic macroinvertebrate surveys
380
Quantitative physical habitat assessment