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Public Information Session Community Government of Behchoko Type A Water Licence Application November 10, 2014 Purpose of Presentation Community Government of Behchoko is applying to the Wekwezhi Land and Water Board for a Type A


  1. Public Information Session Community Government of Behchoko Type A Water Licence Application November 10, 2014

  2. Purpose of Presentation • Community Government of Behchoko is applying to the Wekweèzhiì Land and Water Board for a Type A Water Licence • Current Water Licence is set to expire in November 2014 • Presentation intended to inform community members of the facilities and activities covered under the pending Water Licence

  3. Proposed New Type A Water Licence Chronology Summer Summer Spring September October November 2014 2013 2014 2014 2014 2014 New Application Old Water Technical Session Final Review WLWB waives Landfill Made to Licence expires and Information comments Public Assessment WLWB and anticipate Requests WLWB meeting Hearing, & Design new Water Anticipate Issue however Licence to be of draft Water requires granted Licence Public Information Session

  4. Items and Facilities Covered Under the proposed Type A Water Licence • Rae Waste Water Treatment Facility (Lagoon & Collection) • Edzo Water Water Treatment Facility (Lagoon & Collection) • Rae Water Intake and Treatment Plant • Edzo Water Intake and Treatment Plant • Solid Waste Management Facility (closure of existing landfill and development of adjacent site) • Spill Contingency Plans • Hazardous Waste Handling • Surveillance Network Program (SNP)

  5. Facilities Subject to Water licence Overview

  6. Rae WWTF location

  7. Rae WWTF Operations Piped to Transfer Residential Storage Station Tanks Vacuum Truck Cell 1: 54,750 m 3 Emergency Overflow June/October via Gate Valve Weir #1 Cell 2: 54,800 m 3 June/October via Gate Emergency Overflow Valve #2 Weir Wetland/Frank Channel

  8. Rae WWTF – Adjustments to SNP Locations

  9. EDZO WWTF Location

  10. Edzo WWTF Operations Lift Station Control Box Cell 1: 1,790 m 3 Cell 2: 1,790 m 3 4 x 20m Dredged Channel 2.1 ha Wetland

  11. Proposed New Solid Waste Facility - History 2006 Study – Dillon Assessed 3 sites for suitability as landfills • Site 1 – Area off access road to Rae • Site 2 – Area off Russel Lake access road • Site 3 – Quarries off Hwy #3 Site 2 was considered the most favourable, however it was recommended that further investigation be completed considering other locations that may be more suitable

  12. Proposed New Solid Waste Facility - History 2009 Study – Aboriginal Engineering Ltd. (AEL) Assessed 5 sites for suitability as landfills • Site 1 – Area off old access road to Rae • Site 2 – Area off Hwy #3 • Site 3 – Tower Hill Quarry site • Site 4 – Quarry site • Site 5 – Existing Landfill Site 2 was selected as the best location and was recommended for construction of a new solid waste facility

  13. Proposed New Solid Waste Facility – Location

  14. Surface Water Flow and Drainage

  15. Proposed New Solid Waste Facility – Site Characterization Geology • The proposed site is characterized by deposits of sands, silts and clays overlain by an organic layer, interspersed with areas of bedrock outcropping. • Overburden thickness at the proposed site ranges from 0.3 m to greater than 2.0 m. • Permafrost was encountered in 8 of 9 test pits and ranged in depth from 0.55 m to 2.0 m • Site not favourable for trench style landfilling

  16. Proposed New Solid Waste Facility – Planning Criteria Assessment

  17. Proposed New Solid Waste Facility – Planning Criteria Assessment

  18. Proposed New Solid Waste Facility – Design 20 year planning horizon requires ~105,000 m 3 of total • compacted waste volume (1.5kg/person/day @ compaction rate of 300 kg/m 3 ) • Proposed site footprint is 245 m * 80 m • Based elevation of site is 160.5 masl with a maximum elevation of 167.5 masl (limits visibility from road)

  19. Proposed New Landfill Footprint

  20. Proposed New Solid Waste Facility – Design Site preparation will require: • Land clearing/grubbing • Cut/fill to maintain consistent base elevation • Berm construction • Granular pad construction

  21. Landfill Design – Site Preparation

  22. Proposed New Solid Waste Facility – Filling Plan Proposed that Site be filled using the lift method • Landfill constructed out of cells (blocks) laid out in strips, lifts and phases. • Width of strips and height of lifts subject to dimensions of active face.

  23. Lift Landfill Components CELLS ACTIVE FACE PHASE 1 FOOTPRINT PHASE 2 FOOTPRINT

  24. Landfill Design – Lift and Phase Approach

  25. Landfill Design – Cross Sections

  26. Proposed New Solid Waste Facility – Opportunities for Extended Life A substantial extension of the life of the landfill may be achieved through the implementation of landfill compaction. This would require a capital investment to acquire suitable machinery, however could substantially increase the site life of the facility.

  27. Closure and Reclamation Plan Existing Site

  28. Closure and Reclamation Plan Existing Site

  29. Closure and Reclamation Plan Existing Site

  30. Closure and Reclamation Plan Existing Site

  31. Closure and Reclamation Plan Existing Site

  32. Existing Landfarm - History Chronology 2009 2013 2004 2014 Landfarm AEL Study and WESA/TEES Depth constructed to partial engaged for delineation and manage PHC rehabilitation feasibility monitoring – impacted soil study of leading to landfarm rehabilitation

  33. Existing Land Farm Assessment

  34. Existing Land Farm Assessment

  35. Existing Landfarm– Feasibility Study Recommendations 1. Material thickness should be decreased to a maximum of 0.5 m to promote volatilization of hydrocarbons. This can be achieved by expanding the land farm footprint, or removing soil that is compliant with the applicable regulations (could be used as cover for the disposal site). 2. The land farm liner should be reconstructed or replaced with an impermeable geosynthetic liner to prevent seepage of PHCs into clean soil below and into the groundwater table. 3. Additional soil delineation below the land farm should be undertaken to assess the extent of deeper impacts. 4. Installation of monitoring wells should be conducted to assess impacts to groundwater. 5. Monthly aeration of impacted soil should be conducted during the snow-free months using the equipment (allu bucket) already available to the public works department. 6. Annual monitoring of PHCs, nutrients and microbial colonies in the treatment area should be conducted at the start of the treatment season and at the end to assess the progress of remediation .

  36. Spill Contingency Plans and Hazardous Waste Management • Details

  37. SNP Program • Details on frequency • Image of SNP locations and purpose

  38. QUESTIONS ?

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