Wolf Creek IA 05-CHA-1339
mouth (S15 T71N R21W Lucas Co.) to confluence with unnamed tributary in E 1/2 NW 1/4 S8 T70N R22W Wayne Co.
- Cycle
- 2024
- Release Status
- Final
- Overall IR
- 5 - Water is impaired or threatened and a TMDL is needed.
- Trend
- Stable
- Created
- 11/1/2023 8:12:27 AM
- Updated
- 2/2/2024 1:55:18 PM
The presumptive Class A1 use remains assessed as "not supported" due to levels of indicator bacteria (E. coli) that exceeded state water quality criteria. The Class BWW2 use was assessed as “not supported” based on biological sampling data and on continuous dissolved oxygen and temperature monitoring data.
Data Sources: Data Source Data Source ID Data Type Data Age Site ID Site Name Site Description USACE 12 WQ CY 2010-2014 15590003 Wolf Creek at CR H50/430th (Site RA-41) USACE 12 WQ CY 2010-2014 15930007 Wolf Creek at CR S23/100th (Site RA-44) Iowa DNR 6 BIO See Below 207 Wolf Creek Chariton Site ID Data Source ID # Samples / # Years 2010 Geometric Mean 2011 Geometric Mean 2012 Geometric Mean Annual Geometric Mean Violation # Violations % Violations Significantly >10% Violations Assessment Type Support Level 15590003 12 19 / 3 959 185 2469 Yes 15 79% Yes Evaluated Not 15930007 12 15 / 3 470 138 632 Yes 8 53% Yes Evaluated Not Site ID Data Source ID # Samples / # Years Maximum Value Mean Value Median Value # Violations % Violations Significantly >10% Violations Assessment Type Support Level 15590003 12 53 / 3 8 7.5 7.6 0 0% No Evaluated Full 15930007 12 35 / 3 8 7.9 7.5 0 0% No Evaluated Full Site ID Data Source ID Parameter Name # Samples / # Years Maximum Value Mean Value Median Value # Acute / Chronic Violations % Acute/ Chronic Violations Significantly >10% Violations Assessment Type Support Level 15590003 12 Ammonia 28 / 3 0.66 0.11 0.05 0 / 0 0% / 0% No Evaluated Full 15930007 12 Ammonia 21 / 3 0.7 0.12 0.05 0 / 0 0% / 0% No Evaluated Full 15590003 12 Chloride 34 / 3 14 6.8 6.4 0 / 0 0% / 0% No Evaluated Full 15930007 12 Chloride 14 / 3 13 7.2 6.7 0 / 0 0% / 0% No Evaluated Full 15590003 12 Dissolved oxygen 53 / 3 11.7 8.3 7.9 NA / 1 NA / 2% No Evaluated Full 15930007 12 Dissolved oxygen 35 / 3 12.3 8.4 8.2 NA / 1 NA / 3% No Evaluated Full 15590003 12 pH 53 / 3 8 7.5 7.6 0 / NA 0% / NA No Evaluated Full 15930007 12 pH 35 / 3 8 7.9 7.5 0 / NA 0% / NA No Evaluated Full 15590003 12 Temperature 53 / 3 27.5 17.1 17.8 0 / 0 0% / 0% No Evaluated Full 15930007 12 Temperature 35 / 3 25.1 16.3 18.1 0 / 0 0% / 0% No Evaluated Full Benthic Macroinvertebrates: Site
ID Date Drainage
Area (mi2) Ecoregion Major
Drainage BM
Sample Gear BMIBI
score BMIBI
Class 40a
BMIBI BIT BMIBI
Pass/Fail 207 9/11/19 65.7 40a MO Surber 37 Fair 41 Fail 207 9/14/15 65.7 40a MO Hess 37 Fair 41 Fail 207 8/3/15 65.7 40a MO Hess 43 Fair 41 Pass Fish: Site
ID Date Drainage
Area (mi2) Ecoregion Major
Drainage Riffle
Stream? FIBI
score FIBI
Class 40a
FIBI BIT FIBI
Pass/Fail 207 9/11/19 65.7 40a MO NA 45 Fair 33 Pass 207 9/14/15 65.7 40a MO NA 17 Poor 33 Fail Overall: Community Assessment
Type Assessment
Result Support
Level IR
Category Reason Benthic Macroinvertebrates Evaluated Fail
(1/3) Not Fish Evaluated Fail
(1/2) Not 5bv Assessment was evaluated because some of the samples used
to complete Overall Evaluated Fail Not the assessment were not collected in the last five years. The results of
continuous dissolved oxygen (DO) and temperature monitoring in 2012 for the
DNR/SHL sampling project do suggest impairment of Class BWW2 aquatic life uses.
The lowest DO concentration recorded in 69 days of continuous monitoring was
2.1 mg/L. The daily DO minimum concentration failed to meet the 24-hour DO
criterion (4 mg/L) in 29 of 69 days and the 16-hour DO criterion (5 mg/L) in 9
of 69 days. The percentages exceeding the 24-hour and 16-hour DO criteria
(42.0% and 13.0%, respectively) were greater than (failing) the 10% impairment
threshold used to assess Binomial water quality parameters. The associated
statistical analysis confidence level for the 24-hour analysis result was high
(>90%), while the confidence level for the 16-hour analysis result was not
high (<90%). The maximum stream temperature recorded during the sensor
deployment period was 34.2 degrees (C). The temperature criterion for warm
water interior streams (32 C) was exceeded in 15 of 69 days. The percentage
exceeding (21.7%) was greater than (failing) the 10% impairment threshold with
high statistical confidence (>90%). Based on these data, the BWW2 aquatic
life use was assessed as impaired for DO and temperature. The assessment type
is “evaluated” because it is based on data collected from a single year within
the current data assessment period. In order to meet the requirements for a
“monitored” assessment, the DNR’s continuous monitoring assessment methodology
requires monitoring data from two or more years within the assessment period.
Presumptive Class A1 - Indicator Bacteria: 2010-2012
Presumptive Class A1 - pH: 2012-2014
Class BWW2 - Binomial Parameters: 2012-2014
Class BWW2 - Biological Sampling:
Class BWW2 – Continuous Monitoring Data: