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Chapter A - Introduction - City of Pickering

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property.<br />

COMMENT MESPA RESPONSE (December 2011) CITY RESPONSE (October 2012) RESPONSE<br />

• Surface Water Hydrology (Section 5.0)<br />

Hydrologic Model<br />

The uncalibrated existing conditions hydrologic model that was developed<br />

for the Seaton MESP (AMEC Model) varied considerably from the<br />

TRCA’s approved existing conditions calibrated Duffins Creek model,<br />

which was updated by Aquafor Beech in 2002 (Aquafor 2002 Model).<br />

Aquafor’s 2002 Model was further discretized by AMEC into 126 different<br />

subcatchments, with the main parameters that affect the calibration <strong>of</strong> a<br />

model being changed using different methodologies (i.e. CN vs. CN*,<br />

different equation used for time to peak, additional route channel<br />

commands, etc.) and no re-calibration <strong>of</strong> the model was completed. While<br />

the need for the extensive discretization completed for the existing<br />

conditions model is unclear, the methodologies used to derive<br />

parameters should be consistent for the entire Duffins Creek model and<br />

should use methodologies, which are appropriate for Southern Ontario.<br />

The time to peak equation used in the calibrated Aquafor 2002 Model<br />

was Watt & Chow’s method, which was developed utilizing streamflow<br />

and precipitation data from Southern Ontario. Through comparing results<br />

from the Aquafor 2002 Model with actual streamflow data, it was<br />

confirmed that this method gave good results for the Duffins Creek<br />

watershed. Notwithstanding that, the MESP states that AMEC used the<br />

HYMO equation to calculate the time to peak in their analysis. It is<br />

unclear why this equation was used instead <strong>of</strong> Watt & Chow’s method<br />

given that the OTTHYMO-89 and VO2 literature, as well as other reports,<br />

state that the HYMO equation gives erroneous results in Southern<br />

Ontario unless it is calibrated using local streamflow and precipitation<br />

data.<br />

The reason for the discrepancies given in the literature is that the<br />

regression constants in the HYMO equation were developed using data<br />

collected from farm fields in the southern United States. Given the<br />

inherent difficulties with transposing methods derived from differing<br />

climatic and physiographic regions to Southern Ontario, it does not<br />

appear as though the proponent has completed the rigorous technical<br />

analysis required to support the use <strong>of</strong> the HYMO method in the Duffins<br />

Creek watershed.<br />

whether the ro<strong>of</strong> leaders are connected and the flows<br />

are conveyed by clean water collector to a centralized<br />

infiltration facility. This detail will be worked out through<br />

the NFSSRs. The text has been clarified to make this<br />

distinction.<br />

An update to the hydrologic model has been undertaken<br />

as per discussions at technical meetings with TRCA and<br />

the <strong>City</strong>.<br />

Briefly, the approach agreed upon involves using the<br />

2002 existing conditions model as the base for the 2 –<br />

100 year and Regional Storm event modelling, with<br />

minor changes only to boundaries within the Seaton<br />

lands, based on more current mapping, and the creation<br />

<strong>of</strong> discrete subcatchments for each <strong>of</strong> the different<br />

subwatersheds, to enable accurate comparisons at<br />

varying points in the watershed. All changes have been<br />

made using the 2002 methodology for parameterization<br />

and retaining the CN values from the 2002 model as per<br />

direction from TRCA and the <strong>City</strong> <strong>of</strong> <strong>Pickering</strong>. The one<br />

variable changed for calibration purposes, as discussed<br />

with the TRCA and <strong>City</strong>, was that N has been lowered<br />

from 1.5 to 1.45 in order to reproduce the currently<br />

approved flow rates as per the requirements <strong>of</strong> the<br />

TRCA and the <strong>City</strong> <strong>of</strong> <strong>Pickering</strong>.<br />

In addition, the models have all been validated by<br />

assessing their performance with additional suitable<br />

historical rainfall and streamflow records found within<br />

the data provided by TRCA (2002 to present).<br />

In terms <strong>of</strong> the Regional Storm model for future<br />

development conditions, discussions with the TRCA and<br />

<strong>City</strong> <strong>of</strong> <strong>Pickering</strong> staff have occurred throughout 2011 to<br />

identify a modelling approach and alternative potential<br />

management scenarios, and review updated existing<br />

conditions model results. These discussions are<br />

ongoing and will continue over the next few months.<br />

The conclusion <strong>of</strong> these discussions and analyses will<br />

make specific recommendations regarding a Regional<br />

Storm Control Strategy, if needed to minimize or reduce<br />

risks to human life and property due to flooding.<br />

No further action required from the SLG. All<br />

issues related to the previously submitted<br />

hydrology model is being dealt with through the<br />

2012 Duffins Hydrology Update.<br />

The SLG will be responsible for achieving the<br />

required level <strong>of</strong> SWM control, as recommended<br />

in the hydrology update.<br />

frontages less than 12m, is acknowledged.<br />

The PRMS model showed that having<br />

disconnected ro<strong>of</strong> leaders was a “tool” in<br />

the “LID toolbox” that would help to achieve<br />

the required mitigation. Going forward, the<br />

on-going PRMS modelling is looking at the<br />

potential implication to removing<br />

disconnected ro<strong>of</strong> leaders for lots less than<br />

12m frontage.<br />

REPORT CHAPTER<br />

AND SECTION<br />

No response required. <strong>Chapter</strong> B5.0<br />

Unless there is a clearly demonstrated need to change the method used<br />

to calculate the time to peak, the proponent should use the Watt & Chow<br />

method to ensure consistency with the rest <strong>of</strong> the Duffins Creek model<br />

The higher-discretized model has been used for the<br />

future land use with SWM condition to allow for peak<br />

flow calculations at each SWM facility and channels<br />

The Sernas Group Inc., Stonybrook Consulting Inc. December 2011, Revised February 2013 Master Environmental Servicing Plan - Amendment<br />

SPL Beatty, Bird and Hale Limited, Earthfx Inc. 07161 Seaton Community, <strong>City</strong> <strong>of</strong> <strong>Pickering</strong><br />

AMEC Earth & Environmental, R.J. Burnside Appendix A7 – Page 7<br />

Amos Environment + Planning

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