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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 />

application, methods of increasing public awareness of the environmental impacts of<br />

road salt, <strong>and</strong> the effectiveness of municipal Salt Management <strong>Plan</strong>s.<br />

3.5.3 Agriculture<br />

<strong>Subwatershed</strong> modelling (that excludes atmospheric) indicates that 27% <strong>and</strong> 34% of<br />

phosphorus loads can be attributed to agriculture in the Hewitt’s <strong>and</strong> <strong>Lovers</strong> <strong>Creek</strong><br />

subwatersheds, respectively. Recent water quality monitoring (2008 to 2010) within these two<br />

creeks has shown that phosphorus concentrations regularly exceed the provincial st<strong>and</strong>ards.<br />

Considering the current concentrations of phosphorus in Hewitt’s <strong>and</strong> <strong>Lovers</strong> <strong>Creek</strong>, <strong>and</strong> the<br />

high proportion that can be attributed to agricultural sources, actions leading to reduction in<br />

agricultural phosphorus loads to these two creeks is a priority.<br />

Within the current management framework, the Nutrient Management Act contains the most<br />

stringent policies related to agriculture, as it requires plans for the management of nutrients<br />

created <strong>and</strong>/or stored on farms. Other policies relate to the protection of agricultural resources,<br />

but few relate to the management of nutrients from agricultural areas, with only ‘have regard to’<br />

statements encouraging the use of agricultural BMPs.<br />

Although there are currently no requirements for farmers to undertake BMPs such as cover<br />

crops, conservation tillage, the planting of windrows, <strong>and</strong> leaving riparian buffers intact, there<br />

are a number of available programs to assist farmers to implement these programs. In<br />

particular, the Environmental Farm <strong>Plan</strong> program <strong>and</strong> LSRCA’s L<strong>and</strong>owner Environmental<br />

Assistance Program (LEAP) provide guidance <strong>and</strong> funding for a number of types of projects.<br />

Other gaps in current management include policies requiring livestock to be fenced <strong>and</strong> kept out<br />

of watercourses, an activity that causes numerous water quality issues as well as causing bank<br />

instability.<br />

Recommendation 3-15 - That the subwatershed municipalities, through the LSRCA,<br />

create a roundtable made up of municipalities, LSRCA, MOE, MNR, OFA, NGOs, <strong>and</strong><br />

related l<strong>and</strong>owner representatives, or through existing frameworks such as the Lake<br />

Simcoe Stewardship Network, to determine co-operative ways of implementing<br />

phosphorus reduction <strong>and</strong> improved water quality measures in Hewitt’s, <strong>Lovers</strong>, <strong>and</strong><br />

Innisfil <strong><strong>Creek</strong>s</strong>, <strong>and</strong> to develop an ‘action plan’ for their implementation within the<br />

agricultural <strong>and</strong> rural communities.<br />

Recommendation 3-16 - That the spatially-explicit tool to be developed under<br />

Recommendations 5-7 <strong>and</strong> 5-8 (Chapter 5 – Aquatic Habitat) be used to prioritize<br />

allocation of stewardship resources, so that funds are provided in locations where<br />

maximum phosphorus reduction can be achieved.<br />

Note that unrestricted livestock access <strong>and</strong> its related impacts were reported on <strong>and</strong> remedial<br />

actions are recommended as part of the implementation of agricultural BMPs in Chapter 5 -<br />

Aquatic Natural Heritage. Recommendations 5-7 <strong>and</strong> 5-8 are most relevant to the concern.<br />

3.5.4 Water Temperature – thermal degradation<br />

Increases in stream temperature in the subwatersheds, whether they are due to impervious<br />

surfaces, lack of riparian vegetation, reduction of groundwater contributions, or climate change,<br />

negatively affect the distribution <strong>and</strong> existence of coldwater species like brook trout <strong>and</strong> mottled<br />

sculpin due to their restrictive thermal requirements.<br />

Recommendation 3-17 – That, as new or retrofit stormwater facilities are constructed,<br />

LSRCA work with subwatershed municipalities to reduce potential thermal impacts of<br />

Chapter 3: Water Quality – Surface <strong>and</strong> Groundwater 134

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