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Barrie Creeks, Lovers Creek, and Hewitt's Creek Subwatershed Plan

Barrie Creeks, Lovers Creek, and Hewitt's Creek Subwatershed Plan

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The <strong>Barrie</strong> <strong><strong>Creek</strong>s</strong>, <strong>Lovers</strong> <strong>Creek</strong> <strong>and</strong> Hewitt’s <strong>Creek</strong> <strong>Subwatershed</strong> <strong>Plan</strong><br />

5.3.7 Loss of riparian vegetation<br />

While many policies now afford some protection to the riparian areas adjacent to the<br />

watercourses, this has not always been the case. In many instances, vegetation in the riparian<br />

areas of the subwatershed’s watercourses has been removed to accommodate urban<br />

development <strong>and</strong> agricultural activities, leaving the bank vulnerable to erosion due to the<br />

removal of the stabilizing influence of the roots of the vegetation. This can result in inputs of<br />

sediment into the watercourse, which can settle <strong>and</strong> smother the substrate, thus eliminating<br />

important habitat used by fish for spawning <strong>and</strong> inhabited by benthic invertebrates. Sediment in<br />

suspension in the water can also interfere with the feeding of those fish species that are visual<br />

feeders.<br />

Riparian vegetation is also an important source of allochthonous material such as leaves <strong>and</strong><br />

branches that serve as a food source for benthic invertebrates, <strong>and</strong> can also provide cover for<br />

fish.<br />

In addition, riparian vegetation serves to enhance water quality – it filters the water flowing<br />

overl<strong>and</strong>, causing sediment <strong>and</strong> other contaminants to settle out or be taken up prior to reaching<br />

the watercourses; <strong>and</strong> also helps to moderate water temperatures through the shade it<br />

provides. Removal of this vegetation can have an influence on the type of aquatic community<br />

able to inhabit the watercourse – a reach that may have been able to support a healthy<br />

coldwater community may no longer be able to do so, <strong>and</strong> the community may shift to cool or<br />

warm water community containing less sensitive species.<br />

5.3.8 Water quality <strong>and</strong> thermal degradation<br />

Inputs of contaminants, including high levels of chloride <strong>and</strong> suspended sediment, to<br />

watercourses can be harmful to many species of fish <strong>and</strong> benthic invertebrates, particularly the<br />

more sensitive species. It can force them to leave their habitats, inhibit their growth, or cause<br />

die-offs if concentrations of a contaminant get too high.<br />

Specific information on water quality issues pertaining to these subwatersheds can be found in<br />

Chapter 3 - Water Quality.<br />

Thermal degradation of a system can be caused by a number of factors. The first is the removal<br />

of riparian vegetation <strong>and</strong> the shade that it creates. If large portions of a watercourse are<br />

shaded, these areas may be key in maintaining cold or cool water temperatures or may be a<br />

refuge for cool or cold water aquatic species during the hot summer temperatures. Runoff can<br />

also cause thermal degradation in a system. As impervious surfaces (such as pavement) heat<br />

up from the sun they easily warm any water running over them, creating a warm water source<br />

as the water drains into a watercourse, possibly rendering the surrounding waters uninhabitable<br />

for coldwater species. Lastly, the detention of water in a pond creates a source of warm water<br />

into a system as it increases the surface area of the water that is exposed to sunlight, <strong>and</strong><br />

keeps it there for a prolonged period of time, leading to warming. Although online ponds are the<br />

greatest concern due to their direct impact on the watercourse, offline ponds (including<br />

stormwater ponds <strong>and</strong> detention ponds for irrigation) that discharge to watercourses are also a<br />

concern.<br />

Figure 5-13 illustrates the OMNR approved temperature designation of the creeks (<strong>and</strong> the<br />

temperature at which they are managed at based on timing restrictions for in-water works) with<br />

current temperature ratings. Where the current ratings differ from OMNR designations (i.e. cool<br />

or warm water readings on cold water system) it indicates that the creek is experiencing thermal<br />

degradation.<br />

Chapter 5: Aquatic Natural Heritage 233

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