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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 />

3.2.2.1.<br />

Temperature Collection<br />

The MNR/DFO protocol (“A Simple Method to Determine the Thermal Stability of Southern<br />

Ontario Trout Streams” (Stoneman, C.L. <strong>and</strong> M.L. Jones 1996), Figure 5-1 in Chapter 5 -<br />

Aquatic Natural Heritage) suggests that trout streams are considered to be coldwater if they<br />

have an average maximum summer temperature of approximately 14°C. Cool water sites are<br />

considered to have average maximum summer temperatures of 18°C. Warm water sites have<br />

an average maximum daily water temperature of 23°C.<br />

To monitor these temperatures, electronic data loggers are installed throughout the Lake<br />

Simcoe watershed during the hot summer months. They are installed in late May/early June <strong>and</strong><br />

then retrieved in late September/early October each year. The loggers are used to monitor the<br />

daily fluctuations in water temperature of the watercourse over the summer. They are set to take<br />

a temperature reading every hour for the entire study period. Periodic checking of the loggers<br />

throughout the summer is necessary for quality control purposes. Once the loggers are retrieved<br />

in early fall from the various stream locations, the data is downloaded <strong>and</strong> then compared to the<br />

air temperature data over the same period of time. Using an Excel spreadsheet, the maximum,<br />

minimum, <strong>and</strong> mean temperatures for each day are graphed. There is some emphasis placed<br />

on the daily high temperatures <strong>and</strong> average maximum temperatures specifically in cold water<br />

stream conditions. The streams can then be classified as cold, cool or warm (see Chapter 5 -<br />

Aquatic Natural Heritage, for figure displaying temperature of creeks). Daily minimum stream<br />

temperatures are used to observe stream recovery from periods of extended warming <strong>and</strong> the<br />

influence of groundwater/baseflow in the individual system.<br />

The LSRCA has been collecting temperature data for approximately five years in <strong>Barrie</strong> <strong><strong>Creek</strong>s</strong><br />

<strong>and</strong> seven years in <strong>Lovers</strong> <strong>and</strong> Hewitt’s <strong><strong>Creek</strong>s</strong> (Note: data has been collected to characterize<br />

the watercourses, so for some sites this means data has only been collected once, while others<br />

that are being monitored for long term trends are collected every year). While this has been<br />

sufficient for increasing our underst<strong>and</strong>ing of where coldwater systems are found in the<br />

subwatershed, it is difficult at this point to see any trends or patterns in the data for most sites.<br />

There are factors influencing water temperature in addition to upstream <strong>and</strong> surrounding l<strong>and</strong><br />

use, including air temperature <strong>and</strong> the amount of precipitation, which make it difficult to analyze<br />

trends in water temperature.<br />

3.2.2.2. Beach Monitoring<br />

Public beaches in the City of <strong>Barrie</strong> <strong>and</strong> Town of Innisfil are monitored every year, from June<br />

until the end of August, to ensure that the water is safe for swimmers (in terms of bacteria).<br />

Typically, a there is a minimum of five sampling sites at each beach that are spread out to be<br />

representative of the whole beach area. Samples are normally taken once a week, but<br />

additional samples will be taken under certain<br />

conditions. Samples are sent to the Provincial<br />

Laboratory <strong>and</strong> analyzed for E. coli bacteria (key<br />

indicator of fecal pollution). Other parameters are<br />

not tested for unless deemed necessary. Additional<br />

data that is recorded at the time of sampling<br />

includes weather conditions, whether there was rain<br />

in the previous two days, wind direction, degree of<br />

wave action, number of bathers, number of water<br />

fowl <strong>and</strong>/or animals in the area, <strong>and</strong> clarity of the<br />

water (Simcoe Muskoka Health Unit, 2011).<br />

Chapter 3: Water Quality – Surface <strong>and</strong> Groundwater 80

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