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Lake Erie North Shore Watershed Plan - Niagara Peninsula ...

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LAKE ERIE NORTH SHORE WATERSHED PLAN<br />

Carolinian Canada‟s „Big Picture‟ identifies existing natural cores, corridors and potential<br />

linkages in Canada‟s Carolinian life zone while Regional <strong>Niagara</strong>‟s Core Natural<br />

Heritage System consists of core natural areas to <strong>Niagara</strong> Region and potential linkages<br />

to areas identified as core areas. These layers and all subsequent layers were used in<br />

the analysis and identification of potential restoration areas in the <strong>Lake</strong> <strong>Erie</strong> <strong>North</strong> <strong>Shore</strong><br />

<strong>Watershed</strong>.<br />

The criteria for each restoration category (riparian, wetland and upland) were derived<br />

from several sources including Environment Canada‟s (2004c) framework for guiding<br />

habitat rehabilitation (Appendix G).<br />

Each type of habitat restoration (riparian, wetland, upland) has been prioritized as most<br />

suitable, moderately suitable or least suitable. Areas suitable for riparian, wetland and<br />

upland habitat restoration may overlap on the following watershed restoration strategy<br />

maps due to the methodology from which they were derived. When this occurs, the most<br />

suitable restoration project should be implemented based on field verification, available<br />

project funding, landowner partnerships as well as the opportunity to enhance ecological<br />

linkages.<br />

Restoration Suitability Mapping<br />

The criteria used to create the restoration suitability mapping were derived from several<br />

sources (Appendix H). The criteria for each restoration category (riparian, wetland and<br />

upland) vary and have been weighted differently based on the suitability of the land for<br />

habitat creation. A complete list, including the rationale, methodology and reference for<br />

each criterion used in the suitability analysis are presented in Appendix H, and the top<br />

three criteria for each restoration category are presented below.<br />

Riparian Habitat Restoration Suitability<br />

The criteria used to identify riparian habitat restoration suitability include, for example,<br />

stream bank erosion rates. This criterion is used because riparian areas identified as<br />

having high erosion rates resulting from an upslope contributing area and slope gradient<br />

analysis are most suitable to restoration with bioengineering. The proximity to a<br />

watercourse or waterbody identified riparian suitability because these areas contribute to<br />

both riparian buffers and floodplains, and restoration in these areas will improve the<br />

hydrological, habitat and water quality functions in the watershed. Land use type is<br />

ranked third in terms of identifying suitable areas for riparian restoration. Areas classified<br />

as scrub, low intensity agriculture, or natural areas are much more suitable to restoration<br />

than areas classified as industrial or urban.<br />

Wetland Habitat Restoration Suitability<br />

The criteria used to identify wetland habitat restoration suitability include, for example,<br />

soil drainage because the drainage class of an underlying soil determines the amount of<br />

water the soil can receive and store before runoff. The more poorly drained the<br />

underlying soil, the more suitable the area is for wetland restoration. The wetness index<br />

predicts zones of water saturation where steady-state conditions and uniform soil<br />

properties are assumed. Similar to riparian restoration, land use type plays a role in<br />

determining areas suitable for wetland restoration.<br />

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