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Chapter A - Introduction - City of Pickering

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Comments in white are satisfied.<br />

Comments in orange background are not satisfied or are new comments.<br />

Comments in blue background can be addressed at the NFSSR stage.<br />

Comments in yellow are deferred due to need for hydrology model.<br />

APPENDIX A. TRCA COMMENTS ON SEATON MESPA DECEMBER 2011; MESPA TEAM RESPONSE FEBRUARY 2013<br />

# Section #<br />

Page # in<br />

PDF TRCA Comment Action Required<br />

Consulting Team’s Response<br />

April 27, 2011<br />

Action Taken<br />

MESPA December 2011<br />

TRCA Comment on MESPA<br />

Team Response<br />

February 2013<br />

HY066 West Duffins At Highway 7<br />

HY082 Reesor Creek @ 8th Conc.<br />

Rain Gauges<br />

HY001 Ajax Works Yard<br />

HY031 Goodwood Pumping Station<br />

HY015 Claremont Shop<br />

HY051 Petticoat CA<br />

HY043 Reesor Creek near Highway 7<br />

NEW 1 5.9.3.3 111 Section B5.9.3.3 states that LID measures are<br />

incorporated into the model by reducing the<br />

impervious area to account for the run<strong>of</strong>f<br />

reduction, but section B2.3.2 states that the<br />

depression storage was increased. Please<br />

provide details on the process <strong>of</strong> accounting for<br />

LIDs in the model in the QUALHYMO section –<br />

what % decrease in run<strong>of</strong>f or depression storage<br />

increase was used for each practice. This is not<br />

explicit in Section B4.7 and should be clarified.<br />

Clarify process.<br />

Prepare a table based on land use, LID method<br />

and drainage catchment and neighbourhood #.<br />

HY009 Brock West Landfill<br />

The third paragraph <strong>of</strong> Section B2.3.2 <strong>of</strong><br />

the 2011 MESPA states the following: “The<br />

percent reduction in surface run<strong>of</strong>f volume<br />

from the PRMS model was then<br />

incorporated into the QUALHYMO model.”<br />

The PRMS model looked at depression<br />

storage for modelling <strong>of</strong> the LID measures<br />

so maybe that is the confusion. A table<br />

has been referenced in Section B5.2.3.5<br />

and provided in Appendix B5-B.<br />

A tabular format based on land use, LID method<br />

and drainage catchment or neighbourhood would<br />

be helpful.<br />

NEW 2 5.9.3.4 The Whitevale Creek Erosion Assessment states<br />

that “there will be minimal change in erosion<br />

potential in this location during frequent storm<br />

events regardless <strong>of</strong> whether or not quantity<br />

controls are provided on SWMFs within the<br />

subwatershed.” (p. 115)<br />

Update based on hydrology.<br />

Refer to Section B5.3 <strong>of</strong> the revised<br />

MESPA.<br />

Given that quantity controls are designed to<br />

reduce peak flows during less frequently occurring<br />

events, it would follow that the quantity control<br />

component <strong>of</strong> a SWM pond would have little to no<br />

impact on frequently occurring events. Thus, this<br />

statement is misleading.<br />

Even if the analysis for Whitevale Creek can show<br />

that flood impacts can be mitigated, the TRCA<br />

does not support QUALHYMO as an effective<br />

measure for determining the impacts <strong>of</strong> less<br />

frequent storm events on erosion. TRCA has<br />

experienced significant creek erosion that has<br />

occurred during single large events (August 19,<br />

2005), and are concerned that these impacts are<br />

not being properly addressed as part <strong>of</strong> this<br />

analysis.<br />

More will be known about the proposed changes<br />

in flow when the hydrology model is updated,<br />

however, current information shows that the<br />

proposed 2 year rainfall event is greater than the<br />

pre development 100 year event. TRCA expect<br />

PAGE 8 February 2013

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