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HomeMy WebLinkAbout20211005_NCWRC_CommentsQ North Carolina Wildlife Resources Commission 9 Cameron Ingram, Executive Director MEMORANDUM TO: Adam Parr Assistant State Mining Engineer Land Quality Section - FROM: Olivia Munzer, Western Piedmont Coordinator Habitat Conservation DATE: 05 October 2021 SUBJECT: New Mining Permit Application for Carolina Lithium Mine, Gaston County, North Carolina Biologists with the North Carolina Wildlife Resources Commission (NCWRC) have reviewed the subject permit application. Our comments are provided in accordance with provisions of the Mining Act of 1971 (as amended, 1982) (G.S. 74-46 through 74-68 15 NCAC 5). Piedmont Lithium Carolinas, Inc. has applied for a new mining permit for the proposed Carolina Lithium Project centered around 1501 Hephzibah Church Road in Bessemer City, Gaston County, North Carolina. The project consists of the Concentrate Operations (mine operations) and the Lithium Hydroxide Concentrate Plant (processing operations). The total acreage of the site is 1,548, of which 719 acres (ac) will be disturbed by tailings/sediment ponds (20 ac), stockpiles (21 ac), wastepiles (119 ac), processing area/haul roads (137 ac), mine excavation (403 ac), and other (19 ac). Little Beaverdam Creek, Beaverdam Creek, and their unnamed tributaries in the Catawba River basin flow through the proposed site. Beaverdam Creek and Little Beaverdam Creek are classified as a Water Supply IV stream by the NC Department of Water Resources (NCDWR). We have records for the dwarf -flowered heartleaf (Hexastylis naniflora; Federal Threatened, State Threatened), bigleaf magnolia (Magnolia macrophylla; State Threatened), bog turtle (Glyptemys muhlenbergii; Federal Threatened Due to Similarity of Appearance; State Threatened), Virginia spiderwort (Tradescantia virginiana; State Threatened), dwarf threetooth (Triodopsis fulciden; State Special Concern), and bald eagle (Haliaeetus leucocephalus; State Threatened), which is protected by the federal Bald and Eagle Protection Act, in the vicinity of the site. State significantly rare species found in the area include seagreen darter (Etheostoma thalassinum), Carolina foothills crayfish (Cambarus johni), striate button (Mesomphix pilsbryi), glade milkvine (Matelea decipiends), and Georgia holly (Ilex longipes). Additionally, an undescribed crayfish occurs in Beaverdam Creek downstream of the project, and several state -listed aquatic mussels may occur in or downstream of the site. HDR conducted surveys Mailing Address: Habitat Conservation Division • 1721 Mail Service Center • Raleigh, NC 27699-1721 Telephone: (919) 707-0220 • Fax: (919) 707-0028 Page 2 05 October 2021 Piedmont Lithium Mine Permit Application Gaston County for federally protected species, and none were observed within the proposed mine site. Additionally, the Eaker Farm Catawba Land Conservancy Easement occurs adjacent to the proposed site. We have concerns for the direct and indirect impacts to aquatic and terrestrial resources in and adjacent to the proposed project. Furthermore, we have provided some recommendations to minimize impacts to aquatic and terrestrial wildlife resources. The Groundwater Model Dewatering Simulations Technical Memorandum indicates that the operations of the mine will change groundwater flow into wetlands on site and the baseflow of streams; however, the impacts on streams and wetlands outside the site are not discussed. Although water withdrawn during the operation will be returned to streams at NPDES permitted discharge points, we have concerns for the impact of the mine operation from the dewatering of streams and wetlands outside the site, including downstream, and the effect on aquatic and terrestrial organisms. 2. We are concerned with the riparian and wetland buffer extending only 30 feet, per the Gaston County Unified Development Ordinance. We are concerned that 30 feet will not provide enough buffer to maintain stream bank stability and minimize erosion, especially during flooding; the treatment of pollutants and sediments from the mining operation from entering streams and wetlands; and providing travel corridors for wildlife. We recommend a minimum 100-foot undisturbed buffer for perennial streams and a 50-foot undisturbed buffer for intermittent streams and wetlands. We are pleased to see NC Steep Slope Mix will be used for revegetation of the site. Rather than the Flat Pea/Perennial Pea Mix (ERNMX-112), we would prefer one of the Native Steep Slope Mix (ERNMX- 1810-2) or Ernst Native Habitat for Strip Mines Mix (ERNMX-111) because flat pea is a non-native species with invasive tendencies. Alternative legumes to flat pea are ticktrefoil (Desmodium spp.) or partridge pea (Chamaecrista spp.), both of which are included in the recommended native mixes. 4. Minimize removal of native trees and shrubs during construction. If buffers need to be replanted (pg. 14, Section 10a.), we recommend planting native species, such as a mix of hardwood and pine trees. 5. We recommend monitoring water quality, and perhaps surface flow downstream of the project and/or discharge point. 6. Ensure all stormwater outlets are drain through a vegetated upland area prior to reaching any stream or wetland area. Sufficient retention designs should be implemented to allow for the slow discharge of storm water, attenuating the potential adverse effects of storm -water surges; thermal spikes; and sediment, nutrient, and chemical discharges. Ensure erosion control and sedimentation basins and associated structures (i.e., dissipater pads) are located outside the recommended stream buffers, which are a minimum 100-foot for perennial streams and a 50-foot for intermittent streams and wetlands. 7. We appreciate that bridges will be used for stream crossings, but the design could cause potential erosion could result from the current design. The spans are set on footers, which could cause bank disturbance during construction, and after construction, the minimal daylight under the structure prevents vegetation from growing and causing unstable banks. To prevent the banks from eroding, the span width could be increased to move the footers away from the top of bank, or use a boulder toe stream restoration structure, or something similar, to maintain normal channel width. Secondly, use onsite material excavated during bridge construction to backfill the spans to match the floodplain elevation. Lastly, ensure the bridge is aligned appropriately with the floodway to reduce erosion during high flow. Also, consider that flood debris can catch on the Page 3 05 October 2021 Piedmont Lithium Mine Permit Application Gaston County abutment of the spans and the rack buildup can destabilize the stream bank and effect sediment transport. 8. Avoid clearing the proposed project from roughly March through August, which includes the migratory bird nesting season and maternity roosting season for bats. 9. Heavy equipment should be operated from the stream bank rather than in the stream channel to minimize sedimentation and reduce the introduction of other pollutants into the stream. 10. All mechanized equipment operated near surface waters should be inspected and maintained regularly to prevent contamination from fuels, lubricants, hydraulic fluids or other toxic materials. 11. Water discharges from the site should be proportional to the size of the receiving stream so the hydrology of the stream is not altered, and all discharges should comply with NPDES permit requirements. In particular, turbidity of the discharge should be maintained at or below the permit requirement. High water discharge rates and turbidity can negatively impact aquatic resources within and downstream of the site. Excessive silt and sediment loads can have numerous detrimental effects on aquatic resources including destruction of spawning habitat, suffocation of eggs, and clogging of gills of aquatic species. 12. This region is known for underground mine, shafts, and mine -like features that serve as hibernaculum for several bat species. If any mines or mine -like features occur onsite, NCWRC would like to survey the structure prior to construction and exclude any bats to ensure they are not impacted by disturbance. Due to white -nose syndrome, populations of bat species that use mines and caves have declined drastically. Please contact me if these features are present at the mine. 13. Strict sediment and erosion control measures should be installed prior to any land -disturbing activity. The use of biodegradable and wildlife -friendly sediment and erosion control devices is strongly recommended. Silt fencing, fiber rolls and/or other products should have loose -weave netting that is made of natural fiber materials with movable joints between the vertical and horizontal twines. Silt fencing that has been reinforced with plastic or metal mesh should be avoided as it impedes the movement of terrestrial wildlife species. Excessive silt and sediment loads can have detrimental effects on aquatic resources including destruction of spawning habitat, suffocation of eggs, and clogging of gills. 14. We recommend reclaiming the relatively shallow sediment basins as wetlands, where practicable. Thank you for the opportunity to comment. Further information and free technical guidance from the NCWRC is available upon request. For questions or comments, please contact me at (336) 269-0074 or olivia.munzergncwildlihLM. ec: W. Thomas Russ, NCWRC David Miller, NC DEMLR Kelly Thames, HDR Engineering of the Carolinas, Inc.