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Lower Welland River Characterization Report - Niagara Peninsula ...

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Riffle Embeddedness (if applicable):<br />

<strong>Lower</strong> <strong>Welland</strong> <strong>River</strong> Study Area<br />

<strong>Characterization</strong> <strong>Report</strong><br />

If particles along the stream bed are completely or partially embedded then a low<br />

score is assigned to this category.<br />

This information collected for the 2 field sites in the Thompsons Creek watercourse is presented in<br />

the Beaverdams and Shriners Creek Geomorphic Study, including Thompsons Creek report<br />

(NPCA 2010e).<br />

.<br />

Site <strong>Characterization</strong>s<br />

As indicated earlier, during the summer months of 2010 two field sites were assessed along<br />

Thompsons Creek. The results of the field work, as well as possible restoration alternatives are<br />

recorded for each site in the following section.<br />

1. Heartland Forest (TCTa): This field site is within the Provincially Significant Wetland,<br />

Thompsons Creek Wetland. Bank instability is present in the form of undercutting and quite a<br />

few debris jams were noted. A large debris jam was identified on the upstream side of a<br />

footbridge which could indicate that the bridge is constricting the channel. The presence of<br />

algae was noted during a site visit in 2010. Recommendations for this site include monitoring<br />

bank erosion to ensure the banks are adequately stabilized. This can be done by the use of<br />

erosion pins inserted into the bank. Additional sediment may be entering the channel through<br />

bank erosion at the numerous debris jams present along this field site. If these debris jams are<br />

causing more sediment to enter the channel then they should be removed. This can be<br />

determined by monitoring the bank erosion adjacent to the debris jams with erosion pins.<br />

Excessive sediment deposition can cause problems in the watercourse, such as lateral channel<br />

adjustments, increased turbidity, filling in of pools, and impacting fish habitat. Measurements<br />

taken of the foot bridge will determine whether the bridge is constricting the channel. If this is<br />

the case then the bridge should be replaced and properly sized. Water quality should continue<br />

to be monitored due to the presence of algae.<br />

2. Garner Road (TCTb/TCTc/TCMc): Two tributary channels at this field site are classified as<br />

municipal drains named Allanport Drain, class 3. Based on the 1934 aerial photograph the<br />

channel has been altered. The presence of algae, and duckweed were noted during a site visit<br />

in 2010. Turbid water was also noted after a storm event in 2010. The invasive species,<br />

phragmites was identified at this field site and further research should be conducted to<br />

determine whether the phragmites should be removed from this location. Water quality should<br />

continue to be monitored in this watershed.<br />

Watershed Habitat Restoration<br />

Environment Canada (2004) in its How Much Habitat is Enough? document puts forth restoration<br />

guidelines for wetland, riparian, and forest habitat. This framework provides “science-based<br />

information and general guidelines to assist government and non-government restoration<br />

practitioners, planners and others involved in natural heritage conservation and preservation by<br />

ensuring there is adequate riparian, wetland and forest habitat to sustain minimum viable wildlife<br />

populations and help maintain selected ecosystem functions and attributes”. Given the breadth of<br />

science used to generate this framework, its guidelines will serve as the basis for the habitat<br />

restoration recommendations to be implemented through the NPCA Water Quality Improvement<br />

Program. A summary of the riparian, wetland and forest habitat restoration guidelines have been<br />

reproduced in Appendix D.<br />

54

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