APPENDIX Q-3 COMPARISON OF AIR QUALITY ASSESSMENT VERSUS PROPERTY CHANGES. RAINY RIVER PROJECT Final Environmental Assessment Report
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1 APPENDIX Q-3 COMPARISON OF AIR QUALITY ASSESSMENT VERSUS PROPERTY CHANGES Final Environmental Assessment Report
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3 TECHNICAL MEMORANDUM To Kyle Stanfield, New Gold Inc. File no TC From Tony van der Vooren, AMEC cc Sheila Daniel, Dave Simms, Tel AMEC Date October 21, 2013 Subject Rainy River Project: Comparison of Air Quality Assessment versus Property Changes Summary Since the completion of the Air Quality Assessment Report for the Rainy River Project (RRP) in June, 2013, Rainy River Resources / New Gold Inc. has acquired the rights to extra property and updated their operational site plan to reflect the additional site area. Overall the changes will reduce the off-property impacts of the mining operation. The extra property provides a further buffer to the site boundary. Impacts predicted in the Air Quality Assessment Report are therefore conservative and over predict the impacts of the most recent site plan and property plan. As the impacts are reduced from the initial assessment, AMEC does not recommend reassessing the potential impacts. The findings of the air quality assessment were as follow: All modelled concentrations for pollutants released during the operation phase of the Project were below applicable Schedule 3 standards of O.Reg. 419 and the Ontario Ambient Air Quality Criteria (AAQC), and demonstrate that the site can operate in compliance with Ontario s regulatory requirements and guidelines; and The cumulative effect, in this case considered to be the combined effect of the background concentrations established for the vicinity of the mine and the effects predicted by the modelling, was considered for each parameter. The potential for an occasional exceedance of the PM 2.5 criteria was identified, which may occur less than one day per year. For all other contaminants, the resultant cumulative concentrations were found to be less than the respective study criterion. Based upon these findings, the RRP is not expected to have a significant negative effect on local air quality. These conclusions do not change with the changes to the property outline. Discussion There are two sets of figures attached to this technical memorandum. The first set is the isopleths for the key contaminants from the Air Quality Quality Assessment. The second set is for the revised site boundaries and site plan, but with the original isopleths. These follow the same number of the original isopleths, but with 'M' preceding the figure number. For example the Total Particulate figure in the Air Quality study is Figure 7-1a. In the second set with the AMEC Americas Limited 2020 Winston Park Drive Oakville, Ontario Canada L6H 6X7
4 Rainy River Project Technical Memorandum: Air Quality Assessment versus Property Changes October 21, 2013 modified site and boundary plans, the equivalent Total Particulate figure is Figure M7.1a. The second set shows isopleths within the new site boundary (i.e. the original receptors), to demonstrate the differences with the new site boundary. Key conclusions from comparing the two sets of isopleths are: 1. The areas immediately to the east and south of the eastern mine rock pile, are now part of the property. Particulate impacts of the east mine rock pile are now substantially less at these off-property locations and boundaries. The following two images of the particulate figures, show the original site boundary and the new boundary. Although the mine rock pile footprint has changed (i.e. moved further east), the modelled impacts to the east and south show significant reductions at the new property boundary. The reduction to the east and south is about 20 to 30 ug/m 3. Impacts to the north of the mine rock pile remain unchanged. The overall maximum for the assessment also changed as a result of the changed plans. In the original assessment, the maximum impact was found at the property boundary shown in the image below. The maximum predicted level for total particulate was 86 ug/m 3. With the revised property boundary, the maximum now occurs to the north of the mine rock pile. The predicted maximum for this location is about 75 ug/m 3. New location of maximum particulate concentration Location of previous maximum particulate concentration
5 Rainy River Project Technical Memorandum: Air Quality Assessment versus Property Changes October 21, There is also a change in footprint for the west mine rock stockpile. In the original assessment, a portion of the mine rock pile was shown to extend slightly off-property. At the time, it was assumed that property would be acquired. This has not occurred, and the mine rock pile has been slightly relocated to ensure the stockpile remains on-site. This is shown in the following two images for the particulate modelling. The activity is now further from the site boundary and will reduce the potential particulate levels at the boundary. 3. The effects of the change in site plan and property boundary are most noticeable in the particulate isopleths. There are off-site reductions as well for NO x, hydrogen cyanide and SO 2, but these are not as significant due to the location of the primary sources for those compounds. The maximum locations have not changed from the previous assessment. Overall, the increased site area has provided extra distance to the off-property receptors, reducing the potential off-property air quality impacts. Changes to the site plan have not caused any differences to modelling assumptions or approach. The original modelling, impact assessment and conclusions are still valid.
6 P:\EM\Projects\2011\TC Rainy River\GIS\EA\EA_FINAL\MXD_Maps\Air_Sources_and_24hrAvg_Particulate_2.mxd N Modelling Property Extent (Feb. 2013) Tailings Management Overburden / West Mine Rock Stockpile (Feb. 2013) Ore / East Mine Rock Stockpile (Feb. 2013) Total Particulate 24 hour average * * Standard is 120 ug/m 3 PROJECT N o : TC Modelled Total Particulate Emissions FIGURE: 7-1a
7 P:\EM\Projects\2011\TC Rainy River\GIS\EA\Air\MXD_Maps\Air_Sources_and_24hrAvg_Particulate_for_TV_2.mxd N RRR Property Boundary to be brought to Lease (Sept. 2013) Tailings Management Overburden / West Mine Rock Stockpile (Sept. 2013) Ore / East Mine Rock Stockpile (Sept. 2013) Total Particulate 24 hour average * * Standard is 120 ug/m 3 PROJECT N o : TC Modelled Total Particulate Emissions FIGURE: M7-1a
8 P:\EM\Projects\2011\TC Rainy River\GIS\EA\EA_FINAL\MXD_Maps\Air_Sources_Particulate_2point5_2.mxd N PM hour average * Modelling Property Extent (Feb. 2013) Tailings Management 3-6 Overburden / West Mine Rock Stockpile (Feb. 2013) Ore / East Mine Rock Stockpile (Feb. 2013) * Ambient air quality criterion is 25 ug/m Modelled PM2.5 Emissions PROJECT No: TC FIGURE: 7-1b
9 P:\EM\Projects\2011\TC Rainy River\GIS\EA\Air\MXD_Maps\Air_Sources_Particulate_2point5_for_TV_2.mxd N RRR Property Boundary (Sept. 2013) to be brought to Lease Tailings Management 3-6 Overburden / West Mine Rock Stockpile (Sept. 2013) 0 PM hour average * Ore / East Mine Rock Stockpile (Sept. 2013) * Ambient air quality criterion is 25 ug/m Modelled PM2.5 Emissions PROJECT No: TC FIGURE: M7-1b
10 P:\EM\Projects\2011\TC Rainy River\GIS\EA\EA_FINAL\MXD_Maps\Air_Sources_and_24hrAvg_HydrogenCyanide_2.mxd N Modelling Property Extent (Feb. 2013) Tailings Management Overburden / West Mine Rock Stockpile (Feb. 2013) Ore / East Mine Rock Stockpile (Feb. 2013) Hydrogen Cyanide 24 hour average* * Standard is 8 ug/m 3 Modelled Hydrogen Cyanide Emissions PROJECT N o : TC FIGURE: 7-2
11 P:\EM\Projects\2011\TC Rainy River\GIS\EA\Air\MXD_Maps\Air_Sources_and_24hrAvg_HydrogenCyanide_for_TV_2.mxd N RRR Property Boundary to be brought to Lease (Sept. 2013) Tailings Management Overburden / West Mine Rock Stockpile (Sept. 2013) Ore / East Mine Rock Stockpile (Sept. 2013) Hydrogen Cyanide 24 hour average* * Standard is 8 ug/m 3 Modelled Hydrogen Cyanide Emissions PROJECT N o : TC FIGURE: M7-2
12 P:\EM\Projects\2011\TC Rainy River\GIS\EA\EA_FINAL\MXD_Maps\Air_Sources_and_24hrAvg_NOx_2.mxd N Modelling Property Extent (Feb. 2013) Tailings Management Overburden / West Mine Rock Stockpile (Feb. 2013) Ore / East Mine Rock Stockpile (Feb. 2013) Nitrogen Oxides 24 hour average* * Standard is 200 ug/m 3 Modelled Nitrogen Oxides Emissions - 24 Hour Average PROJECT N o : TC FIGURE: 7-3
13 P:\EM\Projects\2011\TC Rainy River\GIS\EA\Air\MXD_Maps\Air_Sources_and_24hrAvg_NOx_for_TV_2.mxd N RRR Property Boundary (Sept. 2013) to be brought to Lease Tailings Management Ore / East Mine Rock Stockpile (Sept. 2013) * Standard is 200 ug/m Overburden / West Mine Rock Stockpile (Sept. 2013) Nitrogen Oxides 24 hour average* 7.5 Modelled Nitrogen Oxides Emissions - 24 Hour Average 10 PROJECT No: TC FIGURE: M7-3
14 P:\EM\Projects\2011\TC Rainy River\GIS\EA\EA_FINAL\MXD_Maps\Air_Sources_and_1hrAvg_NOx_2.mxd N Modelling Property Extent Nitrogen Oxides 1 hour average* (Feb. 2013) Tailings Management Ore / East Mine Rock Stockpile (Feb. 2013) Overburden / West Mine Rock Stockpile (Feb. 2013) * Standard is 400 ug/m 3 Modelled Nitrogen Oxides Emissions - 1 Hour Average PROJECT No: TC FIGURE: 7-4
15 P:\EM\Projects\2011\TC Rainy River\GIS\EA\Air\MXD_Maps\Air_Sources_and_1hrAvg_NOx_for_TV_2.mxd N RRR Property Boundary (Sept. 2013) to be brought to Lease Tailings Management Ore / East Mine Rock Stockpile (Sept. 2013) * Standard is 400 ug/m Overburden / West Mine Rock Stockpile (Sept. 2013) Nitrogen Oxides 1 hour average* Modelled Nitrogen Oxides Emissions - 1 Hour Average PROJECT No: TC FIGURE: M7-4
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