Save McDonald Creek
Problems Facing the Creek
Home
Mission
Latest News
Problems Facing the Creek
What You Can Do
Links/Resources
Contact Us

 
Many of the problems that face McDonald Creek are the same as those that are facing most Urban Streams.
 
Increased/decreased flow, habitat Loss, channelization, pesticide and herbicide use are just a few of the many issues that have negatively impacted our waterways.

n696558997_672766_5047.jpg

On the bottom left-hand side, the severely eroded roots of a 60 yr old Cottonwood tree, a favorite of the Great Blue Heron.

n696558997_672764_4397.jpg

Countless numbers of trees have been lost, and with them, the loss of habitat and the potential for further erosion.

n696558997_672763_4082.jpg

Exposed tree roots are seen all along the creek.

img_2402.jpg

img_2394.jpg

Examples of such severe erosion are seen in many places along McDonald Creek. This can increase siltation and affect water quality.

n696558997_672751_62.jpg

Problems Facing Urban Streams

Water Quantity: too little or too much water.

Increased/Decreased Flow:   When rain hits grassy, forested, or other unpaved surfaces, the water soaks into the ground. Much of this water is absorbed by plant roots and is stored in soils. The water that is not absorbed or stored, gradually enters streams and creeks. Stream flow slowly increases to a peak flow, and later slowly decreases to a stable flow maintained by water stored in soils.

When rain hits paved, concreted or other impervious surfaces (rooftops, metal, etc.), the water does not get a chance to filter through the soil. The water immediately becomes runoff. This runoff rapidly moves to the streams and rivers, picking up sediment and pollutants as it travels. Once it reaches the streams and rivers, it causes the water to rise very rapidly and increases the size of the peak flow. This rapid increase flushes fish, insects and other creatures away before they have time to retreat to safe areas.

Particles transported by the rapidly moving water can act as a sandblaster. This process is called scouring. Scouring can undercut root systems and destroy aquatic vegetation and aquatic animals. In addition to the negative effects on larger animals and plants, it can also destroy microscopic animals in the streams. The larger animals, such as fish, eat the microscopic animals. Once the microscopic animals are destroyed, fish no longer have food to survive and prosper.

Large quantities of water flowing quickly through stream channels can cause the banks of the stream to erode, adding sediment to the stream and causing habitat loss. Stream banks may become unstable and fail, resulting in sloughing of adjoining property (such as backyards and roadways). This same increased flow drastically changes the structure of the stream bottom by washing out rocks, logs, and vegetation. These structures provide shelter and food for animals living in the stream.

With more water moving across the land surface and less water making its way into the ground, there is little water being stored in the soils. Consequently, streams are subjected to decreased flow. Water once gradually released from soils is no longer available to maintain stream flows during drier periods. This decrease in flow is also contributing to habitat destruction and causing stream temperatures to increase. Increased stream water temperature results in lowering the ability of the water to carry oxygen. Lower oxygen levels may kill fish.

Habitat Loss - Removal of Riparian Vegetation:  A riparian area is defined as an area of trees, shrubs and other plants located next to, and upslope from, a body of water. Riparian buffer zones are vital to healthy streams, water quality, and healthy ecosystems. Riparian zones provide for the uptake and long term storage of nutrients, water. They also regulate water temperatures by shading the stream, which increases the stream’s ability to hold oxygen. Riparian vegetation also helps filter pollutants and debris, stabilizes stream banks (reducing erosion and sediment transport), and provides for wildlife habitat.

Wetlands:  Wetlands are areas where water is near, at, or above the level of the ground. Biologically, wetlands are rich and diverse ecosystems. Yet, they are often under-appreciated and generally the first to be destroyed by either filling or draining. Wetlands contain plants and microorganisms that help filter excess nutrients and toxins in the water. Wetland areas also retain water, which assists in the prevention of flooding in low-lying developed areas. Wetlands support a large number of threatened and endangered species, including migratory birds, fish, amphibians and wildflowers. Protection of natural wetlands and the construction of new wetlands to replace what was destroyed is key to the development of an effective water quality program and a healthy environment.

Channelization:  Channelization is the practice of dredging and straightening stream channels to increase flow rates and carrying capacities. Channelization acts to force as much water as possible away from an area in a short period of time. Traditionally this was done to prevent flooding. Beargrass Creek concrete channels are a good example. However, there are problems resulting from channelization. Channelization is detrimental for the "well being" of streams and rivers through the elimination of suitable habitat and the creation of excessive flows. Stream bottoms are made more uniform. Habitats of natural streams contain numerous bends, riffles, runs, pools and varied flows, and tend to support healthier and more diversified plant and animal communities than those in channelized streams. A riffle is the shallow area within a stream where the flow of water is constricted and forced over rocks and ledges. Deeper, slow moving water and finer sediments characterize a pool. A run is an area between a pool and a riffle where the water flows a little quicker but is not broken up by rocks and ledges. Historically beaver dams were a very important part of a natural stream habitat. Most channelization and maintenance practices restrict the growth of riparian (streamside) vegetation. This vegetation filters sediments, shades the stream, and provides needed plant materials that seasonally fall into the stream. These plant materials become food and habitat for organisms. The elimination of shading, coupled with the lower water levels, result in temperature elevations of 5-20 degrees Fahrenheit above those found in streams with trees in riparian areas. These temperature elevations create increased stress on fish during the warm weather months due to the warmer water holding less oxygen. Dissolved oxygen stress is common in channelized streams.

Inadequate Substrate:  Substrate describes those materials making up the stream bottom. Normally, riffles, runs, and pools characterize areas within streams. A riffle is the shallow area within a stream where the flow of water is constricted and forced over rocks and ledges. A pool is characterized by deeper, slow moving water and contains finer substrates. A run is an area between a pool and a riffle where the water flows a little quicker but is not broken up by rocks and ledges.

Naturally flowing streams have less erosion and sediment deposition than channelized or flow modified streams. Natural streams tend to create flow patterns containing numerous bends. The inside of a bend usually has finer substrate deposited, while the outside of a bend tends to undercut the bank. This provides shallows in the depositional area and pools in the erosional area. Channelization eliminates these processes and the habitats they create. In most urban streams, excessively increased flow and channelization results in degradation or elimination of the natural substrate and results in decreased habitat diversity.

 

Water Quality

Water Temperature:  Life in the aquatic environment is dependent upon the temperature of the water. For aquatic species, the temperature of the water regulates their life processes (metabolism), their ability to survive, and their ability to reproduce. Water temperature also affects decomposition of biological waste found in both the water and the bottom sediments. Increased decomposition produced by elevated water temperature can cause dissolved oxygen levels to decline, resulting in the death of stream organisms, including fish. Streams suffer from elevated water temperature during the summer months primarily due to the removal of trees along stream banks (riparian area). The loss of shading elevates water temperature in the streams, lowers dissolved oxygen levels and frequently results in fish kills.

pH:  The pH of a stream is the measure of how acidic or basic the water is. If the stream becomes either excessively acidic or basic, it can have a very negative impact on aquatic life. Low pH can be caused by the introduction of organic material during low flows. High pH can be produced by increased photosynthesis (plants using sunlight to create stored energy), or by wash-off of lime applied to croplands, golf courses or lawns.

Total Suspended Solids:  The term total suspended solids (TSS) is a description of the organic and inorganic material suspended in water.  The solids settle out and accumulate on the bottom producing seriously altered streambeds. Interaction between the chemicals in the sediments and the suspended solids reduce dissolved oxygen levels in the water. The accumulation of sediments on the bottom can also eliminate suitable habitat and clog the gills of stream organisms.

Suspended solids originate from construction sites, farms, lawns, streets, parking lots, and commercial sites as storm water washes off of these areas. Suspended solids can also arise from combined sewer overflows, as sewer lines fill with storm water beyond their capacity to transport. Soil erosion is one of our top water quality problems.

Total Dissolved Solids:  Total dissolved solids (TDS) consist of salts, organic matter and dissolved materials. Most aquatic life can tolerate a relatively high range of variation for dissolved solids. However, some dissolved solids can be introduced in sufficient quantities to produce negative impacts on aquatic life. Runoff from streets and parking lots, particularly in winter when salts are applied, can produce aquatic conditions unsuitable for life in streams. Runoff from chemically treated lawns, golf courses and croplands can also produce inhospitable conditions in streams. Lawn chemicals are regularly detected in all of our local streams.

Nutrients:  Nitrogen and Phosphorus found in streams are generally referred to as nutrients. Nutrient levels in most local area streams are often high and result in serious reduction of health in aquatic communities. Typically, high levels of nutrients can arise from a variety of potential sources including treatment plant discharge, septic tank seepage, combined sewer overflows (CSO), sanitary sewer overflows (SSO), runoff of fertilizers, or animal waste products. Nutrients in aquatic systems may result in increased abundance and growth of both rooted vegetation and algae in streams. This problem will increase if trees are removed from stream banks, increasing sunlight and resulting in excessive growth of algae. This excessive growth of algae can cause underlying mats of algae to become shaded, and the result can be mass die off of these underlying mats. The decomposition of dead algae can cause increased oxygen use and result in low dissolved oxygen levels. Fish kills can occur in streams as a result of a combination of elevated water temperature and nuisance levels of algae growth.

Pesticides and Herbicides:  On a seasonal basis, several pesticides and herbicides have been found in stream water, particularly after storm events when they are washed off the surrounding land. They are of concern because, like metals, they can produce toxic effects.

Macroinvertebrate Sampling:   Macroinvertebrates are invertebrates that are large enough to be seen with the naked eye. These may include aquatic insects, snails, clams, mussels, crayfish and worms. The macroinvertebrate community structure can provide information on the health of a stream. Over extended periods of time, the types of macroinvertebrates present can reflect water quality and/or habitat quality of a stream. Among the types of water quality conditions that affect macroinvertebrates are metals toxicity, sedimentation, nutrient enrichment, dissolved oxygen stress, and temperature stress.

Friends of McDonald Creek* Prospect Heights, IL