Development and Application of Coupled Optimization-Watershed Models for Selection and Placement of Best Management Practices in the Mackinaw River Watershed
Agricultural non-point source (NPS) pollution remains to be one of the biggest
challenges in the Midwest due to extensive farming practices and the use of fertilizers to
increase agricultural productivity. Excess sediment and nutrient loadings such as nitrogen
and phosphorous are major causes of non-point source pollution in rivers and streams.
The Mackinaw River watershed, which is one of the tributary watersheds of the larger
Illinois River basin, covers a total drainage area of about 2950 square kilometers. Since
1990, this watershed has been one of The Nature Conservancy’s (TNC) conservation
sites, considered to be an area of biological significance in the Upper Mississippi River
basin. The Mackinaw River watershed plan prepared by The Nature Conservancy in 1998
indicates that altered hydrology and sedimentation are the primary threats to the
Mackinaw River. The plan provided recommendations to improve river hydrology and
reduce sediment yields through changes in the landscape.
Conservation practices serve as crucial control measures in reducing NPS
pollutants from agricultural watersheds. The 2008 Farm Bill provided more than $7
billion for promoting agricultural production and environmental quality by supporting
implementation of structural or non-structural management practices under its
Environmental Quality Incentives Program (EQIP) (Cowan and Johnson, 2008).
Successful implementation of such programs, however, requires sound watershed
management plans. Watershed management plans involving implementation of best
management practices (BMPs) can help reduce pollution from agricultural sources. BMPs
are structural or non-structural control measures that can be implemented in watersheds
to control pollutant loads at their source or their transport to receiving water bodies.
Implementation of these BMPs should focus on critical source areas that may contribute
large amounts of pollutant loads. Identifying areas for the placement of BMPs should take
into account both ecological benefits and associated implementation costs.
The objectives of this study include (1) developing watershed models for
Mackinaw River and two of its tributary watersheds, namely Bray Creek and Frog Alley,
to simulate streamflows and water quality constituent loads, and (2) developing a coupled
optimization-watershed model for cost-effective selection and placement of BMPs in
Bray Creek and Frog Alley watersheds to reduce nonpoint source pollutants such as
sediment and nutrient loads to the streams. An integrated modeling approach that
involves interfacing a simulation model with an optimization algorithm has been
employed to develop the coupled optimization-watershed model. Such integrated
modeling approaches have been demonstrated in solving complex, realistic problems in
the areas of watershed management, reservoir operations, groundwater monitoring
design, and others. In this study, the coupled optimization-watershed model was
developed by interfacing a watershed model known as the Soil and Water Assessment
Tool (SWAT) with Non-dominated Sorting Genetic Algorithm II (NSGA-II), a multiobjective
optimization algorithm. Figure 1 shows the location map of the Mackinaw
River watershed.published or submitted for publicationis peer reviewe