Thor Lake Project DAR Appendix a Stantec Environmental Baseline
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AVALON RARE METALS INC. DEVELOPER’S ASSESSMENT REPORT THOR LAKE PROJECT, NWT APPENDICES VOLUME- 1 THOR LAKE PROJECT, NWT DEVELOPER’S ASSESSMENT REPORT APPENDICES - VOLUME 1 SUBMITTED TO: MACKENZIE VALLEY ENVIRONMENTAL IMPACT REVIEW BOARD MAY 2011 MAY 2011 MVEIRB FILE: EA1011-001 MVEIRB FILE: EA1011-001 Avalon Rare Metals Inc. DEVELOPER’S ASSESSMENT REPORT THOR LAKE PROJECT NORTHWEST TERRITORIES APPENDICES VOLUME 1 Submitted To: MACKENZIE VALLEY ENVIRONMENTAL IMPACT REVIEW BOARD May 2011 LIST OF APPENDICES Volume 1 Appendix A Stantec Environmental Baseline Reports – A1 Volume 2 Appendix A Stantec Environmental Baseline Reports – A2 – A6 Appendix B EBA Baseline and Other Reports Volume 3 Appendix C Knight Piésold Geotechnical, Hydrology, Hydrogeology Reports Volume 4 Appendix D NWT Community Statistics Appendix E Archaeology Study Appendix F SGS Geochemistry/Mineralogy Report Appendix G SENES Radiological Reports Appendix H Avalon’s Traditional Knowledge Study Communication/Consultation Logs Appendix I MVERIB Terms of Reference Appendix J RWDI Air Quality Report Appendix K GSGislason Economic Impact Report Appendix L Avalon Hazardous Materials Spill Contingency Plan APPENDIX A STANTEC ENVIRONMENTAL BASELINE REPORTS Appendix A.1 Thor Lake Rare Earth Metals Baseline Project Environmental Baseline Report: Volume 3 – Aquatics and Fisheries 2010 Appendix A.2 Thor Lake Rare Earth Metals Baseline Project Environmental Baseline Report: Volume 1 – Climate and Hydrology 2010 Appendix A.3 Thor Lake Rare Earth Metals Baseline Project Environmental Baseline Report: Volume 2 – Hydrogeology 2010 Appendix A.4 Thor Lake Rare Earth Metals Baseline Project Environmental Baseline Report: Volume 4 – Terrain, Soils, and Permafrost 2010 Appendix A.5 Thor Lake Rare Earth Metals Baseline Project Environmental Baseline Report: Volume 5 – Vegetation 2010 Appendix A.6 Thor Lake Rare Earth Metals Baseline Project Environmental Baseline Report: Volume 6 – Wildlife Resources 2010 Appendix A.1 Thor Lake Rare Earth Metals Baseline Project Environmental Baseline Report: Volume 3 – Aquatics and Fisheries 2010 THOR LAKE RARE EARTH METALS BASELINE PROJECT Environmental Baseline Report: Volume 3 – Aquatics and Fisheries FINAL INTERIM REPORT Prepared for: Avalon Rare Metals Inc. 130 Adelaide Street Suite 1901 Toronto, ON M5H 3P5 Prepared by: Stantec 4370 Dominion Street, Suite 500 Burnaby, BC V5G 4L7 Tel: (604) 436-3014 Fax: (604) 436-3752 and Stantec P.O. Box 1680, 5021 - 49 Street Yellowknife, NT X1A 2N4 Tel: (867) 920-2216 Fax: (867) 920-2278 Project No.: 123510050 and 123510051 January 15, 2010 Thor Lake Rare Earth Metals Baseline Project Environmental Baseline Report: Volume 3 – Aquatics and Fisheries Final Interim Report Authorship AUTHORSHIP Carey Sibbald, B.Sc., CEPIT .................................................................................................... Aquatics Karen Munro, B.Sc., M.Sc., R.P.Bio. ................................................................ Aquatics Senior Review Sandra Nicol, M.Sc., BIT ........................................................................................................... Fisheries Josh Taylor, M.Sc., R.P.Bio. ............................................................................ Fisheries Senior Review January 15, 2010 i Proposal No. 123510050 and 123510051 Thor Lake Rare Earth Metals Baseline Project Environmental Baseline Report: Volume 3 – Aquatics and Fisheries Final Interim Report Executive Summary EXECUTIVE SUMMARY Avalon Rare Metals Inc. (Avalon) is currently undertaking a prefeasibility study for the development of the Nechalacho Deposit, located on mineral leases it holds at its Thor Lake site in the Northwest Territories. The deposit is located approximately 100 km southeast of Yellowknife and 4 km north of the Hearne Channel of Great Slave Lake. Stantec (formerly Jacques Whitford AXYS Ltd.) initiated environmental baseline studies at the Thor Lake project site in fall 2008. This interim Technical Data Report presents results of the baseline aquatics and fisheries study as of fall 2009. The study investigated water quality, aquatic ecology and fisheries values in nine watercourses and fifteen lakes that will be directly or indirectly affected by Project development. Ten other lakes were also studied: six in the local area to better establish local aquatic conditions and four for use as reference sites. One site in Great Slave Lake was established in an area being proposed for a wharf. Of the nine watercourses studied, three are passable to fish during high flows, two are not passable except during exceptional circumstances (i.e. very high flows), one had visible surface flows but is not passable to fish and three had no visible channels. The quality of the available habitat for fish in these nine watercourses was generally low due to very low water levels. Fish presence was observed in two streams only: a nine-spine stickleback in the outlet of Long Lake and three northern pike in the outlet of Murky Lake. The known fish species in the area primarily use lake habitats; however, northern pike, slimy sculpin and nine-spine stickleback are known to use watercourse habitat as well. These three species spawn in still or slow-moving water and it is unlikely that any of them would fully complete their life cycle in the watercourse habitats of the study area. Littoral and riparian areas of each study lake were examined for predominant aquatic and terrestrial vegetation and fish habitat features (e.g. large woody debris). Substrate in the littoral areas varied from bedrock to organic muck and several species of submerged and emergent aquatic plants were present. Large woody debris and large boulders were often absent. The riparian area of most lakes was dominated by black spruce; other species observed included paper birch, tamarack, dwarf birch and Labrador tea. Wetlands and bedrock bluffs were present or predominant at several lakes. Water and sediment data were collected at 23 study lakes. Water was neutral to basic (mean pH from 7.07 to 8.62), with a large range of conductivity and hardness and low nutrient levels. Large ranges in many general parameters and metals were noted, as levels tended to be elevated during winter in shallow lakes (less than 3 m deep). In shallow lakes during winter, total iron levels were 3 to 61 times higher than the CCME guideline. Sediment characteristics varied across the study area, though generally had relatively high phosphorus, organic carbon and nitrogen content. Arsenic concentrations in sediment exceeded the CCME guideline in many lakes (60% of sample stations), followed by silver (32%), nickel (28%) and copper (16%) exceedances. Data on levels of radionuclides and rare earth elements in lake sediment are not available at this time. Aquatic community data were collected at most sample stations; at the time of this report, phytoplankton and zooplankton data were available for June 2009 but not September 2009, while benthic invertebrate data from September 2009 were not available. Based on chlorophyll a values, ii January 15, 2010 Project No. 123510050 and 123510051 Thor Lake Rare Earth Metals Baseline Project Environmental Baseline Report: Volume 3 – Aquatics and Fisheries Final Interim Report Executive Summary nineteen lakes are considered oligotrophic, four are mesotrophic, and one lake may be eutrophic. Phytoplankton taxon richness (number of taxa per site) varied from 38 to 81 species; richness was greatest at Thor Lake and lowest at Great Slave Lake. Both phytoplankton and zooplankton species diversity was greatest at Porkchop Lake and lowest at Great Slave Lake. Zooplankton taxon richness varied from 13 to 21 species; richness was greatest at A, North Tardiff, South Tardiff and Thor lakes, and lowest at Elbow North and Great Slave lakes. Fisheries studies were conducted in 19 lakes. Of these, 11 are considered fish-bearing. The most common species found were three large bodied species (northern pike, lake whitefish and lake cisco) and two small bodied species (slimy sculpin and ninespine stickleback); all five species were present in Thor, Long, Elbow, A and Redemption lakes. Lake trout was captured only in Carrot and Great Slave (the deepest lakes), while lake chub was captured only in Kinnikinnick Lake. The lakes that are considered non-fish bearing are isolated from other waterbodies and, therefore, do not directly contribute food or nutrients to fish bearing waters; these non-fish bearing lakes are not considered fish habitat under the Fisheries Act. Catch per unit effort (CPUE) was calculated for the large bodied fish species captured in six-panel gang gill nets for 2008 and 2009. CPUE for northern pike and lake whitefish was similar between years, varying by 0.2 fish/hour or less. A decrease in CPUE for lake whitefish was noted for Fred Lake; however, this change is difficult to interpret as this lake suspected to be a sink habitat (fish can enter the lake but do not survive the winter). A change in CPUE for lake whitefish (decrease) and lake cisco (increase) was also noted in A Lake between 2008 and 2009; this change is consistent with known fish habitat use and a change in gear type from sinking to floating gill net. Between 2008 and 2009, there was greater variation in lake cisco CPUE compared to northern pike and lake whitefish; lake cisco appear to form schools, so the catch rate for this species is expected to be more variable than for non-schooling species such as northern pike and lake whitefish. Fish health was assessed. Fish