
Mill Creek Basin
History
The Mill Creek, once named the most endangered urban stream in America by American Rivers , is on its way toward recovery. A few hundred years ago, prior to population growth and development in Cincinnati, there were over 300 miles of creeks and streams in the Lower Mill Creek watershed. These waterways naturally conveyed rainwater from hilltops, down hillsides, and through valleys to the Mill Creek and, eventually, to the Ohio River. As Cincinnati grew, these natural systems were replaced with roads, buildings, and sewer networks. Streams that once followed the natural landscape were directed into over 600 miles of sewer pipes.
Use the slider on the image below to see how the historic landscape differs from what exists today.
Comparison of historical and existing streams
Over the years, industrial pollution and overflows from the combined sewer system destroyed nearly all of Mill Creek’s ecological integrity. However, in recent years, significant strides have been made towards restoring the Mill Creek. This section highlights the monitoring data used to assess the health of the Mill Creek and some of the major initiatives that are contributing to improved water quality.
Stream Condition
Calculations of impairment and attainment of a biological criterion provide quantitative depictions of water quality. In Mill Creek, the results indicate aquatic life conditions have been improving.
These results were published in the Biological and Water Quality Study of Mill Creek 2021 and are further described in this section.
The plots on the right are used to summarize the extent and magnitude of biological impairment or attainment of Clean Water Act goals along the entire length of the mainstem of Mill Creek by year. The zero lines represents the goal (shown in blue). The plots represent two fish measures (IBI, MIwb), the macroinvertebrate measure (ICI), and the overall stream health goal attainment measure.
The Area of Attainment Value (AAV) is calculated as a positive and depicts the extent of criterion achievement. The more area in the top section of the plots (shown in green), the more (full) attainment achieved in Mill Creek.
The Area of Degradation Value (ADV) is calculated as a negative and depicts the extent of impairment (both partial and non-attainment). The more area in the bottom section of the plots (shown in red), the more degradation in the Mill Creek.
Macroinvertebrates are the leading indicator of stream water quality improvement. Macroinvertebrate health are measured using the Invertebrate Community Index (ICI). The improvement since 1992 is shown in the figure below, in which the more area above zero (solid purple), the better the macroinvertebrate community.
IBI is the primary metric for evaluating fish. Improvements in fish community follow, but lag behind the improvement in macroinvertebrate community.
MIwb is a secondary metric for evaluating fish. Improvements also lag behind the macroinvertebrate community.
Overall, the Mill Creek has seen an increase in the number of stream miles attaining biological criteria for aquatic life.
Monitoring Data
Results for ICI, IBI, MIwb, and QHEI by sampling location can be reviewed by clicking on a trend sampling location in the map to the right. An example results graphic is shown below for MC70 IBI.
Chloride
In northern latitudes, chloride has been identified as an emerging problem for aquatic life, largely related to road salt application in developed areas, but some industrial sources in effluents can also contribute. Unfortunately, road salt applied during winter is not exported completely out of a watershed each year and accumulates in soils and shallow groundwater. Because of this chloride levels have been gradually increasing in most developed areas in Ohio. The plot below illustrates a source of chlorides from effluents in the upper part of Mill Creek, but also the increasing general trend in chlorides in the watershed between 1992 and more recent samples.
E. coli
E. coli data is a widely used indicator for fecal contamination in streams and rivers. To protect against gastrointestinal illness when swimming, E. coli measurements in freshwater should not exceed 126 MPN (“most probable number” of bacteria). E. coli, as measured, is generally not a direct health risk, but rather is used as an “indicator” to monitor the presence of more harmful microbes, such as Cryptosporidium, Giardia, Shigella, and norovirus. These microbes are more difficult to measure directly and E. coli can be useful, in a management perspective, to identify sources of contamination.
Featured Projects
MSD is continually seeking to make improvements to its treatment plants and sewer networks. This map shows the location of past and future projects in the Mill Creek.
Some MSD projects are implemented to reduce overflows and improve water quality in the Mill Creek Basin. A few key projects are highlighted in the section below.
Click on the arrows to learn more about each of the projects.