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HomeMy WebLinkAbout20230615_ltr_RFO JCA_re_Knollwood_Apartments_SouthernPinesMooreCounty_s_.pdfUnited States Department of the Interior FISH AND WILDLIFE SERVICE Raleigh ES Field Office Post Office Box 33726 Raleigh, North Carolina 27636-3726 June 15, 2023 Ms. Alicia Jackson Dr. J.H. Carter III & Associates, Inc. 515 F Midland Road Southern Pines, NC 28387 Re: Construction of Knollwood Apartments, Southern Pines, Moore County, North Carolina Dear Ms. Jackson: The Fish and Wildlife Service (Service) has reviewed your May 1, 2023, email, and Biological Assessment titled "Red -cockaded Woodpecker Biological Assessment for the Knollwood Apartments, Southern Pines, Moore County, North Carolina (BA). The proposed action is the construction of a 27-acre apartment complex north of U.S. Highway 1, in the Town of Southern Pines, Moore County, North Carolina. The project falls within the foraging partitions of two active red -cockaded woodpecker (Picoides [=Dryobates] borealis; RCW) clusters. Our comments are provided in accordance with sections 7 and 9 of the Endangered Species Act (Act) of 1973, as amended (16 USC 1531 et seq.) and the Service's Private Lands Guidelines found in Appendix 5 of the Service's Recovery plan for the red -cockaded woodpecker (Picoides borealis): second revision (U.S. Fish and Wildlife Service 2003). The proposed action is the construction of an apartment complex and related amenities on 27 forested acres north of US Highway 1, east of Pine Needles Golf Club and McDeeds Creek, south of Camp Easter Road and McDeeds Creek Elementary School, and west of forested land also owned by Knollwood Partners, LLC, in the Town of Southern Pines, Moore County, North Carolina. The owners plan to construct nine apartment buildings, a clubhouse, a pool, tennis and pickleball courts, a putting green, two parking garages, two retention ponds, a small dog park, and associated driveways, parking areas and sidewalks on the project site. site. A sewer line will also be installed to connect with an existing line and pump station. Other than an existing sewer line, the project site is currently undeveloped and is vegetated with a mixed pine -oak forest. The project falls within the 0.5-mile radius of the foraging partitions for RCW Clusters SOPI 23 and SOPI 22-112. Dr. J.H. Carter III & Associates, Incorporated (JCA) conducted surveys for RCW cavity trees within the 48-acre preliminary project study area and within the 0.5-mile radius foraging partitions of the involved RCW clusters using approved methods in January 2023. JCA also documented the status of RCW cavities/cavity starts in Clusters SOPI 23 and 22-112 in the spring of 2023. The BA summarizes the historical use of the two involved clusters by RCWs for over 40 years. Both clusters contain between 20 and 25 cavity trees with cavities in various stages of completion and suitability. SOPI Clusters 22 and 112 merged into a single cluster many years ago. At least one RCW group has occupied this cluster the entirety of the 40+ year period, including 2023. SOPI 23 was inactive in 2000 and 2001, but has been active every year since 2002. JCA previously conducted a foraging habitat analysis (FHA) for SOPI 22-112 in February 2017. JCA biologists updated stand delineations in April 2019 and February 2023. JCA also updated stand delineations for SOPI 23 in March 2023. The company had stand data from a FHA for this group conducted in 2003. The BA outlines standard for managed stability (SMS) guidance and contains a brief description of stand characteristics for assessing project impacts and making beneficial changes to habitat. Pine stands meeting SMS overstory guidelines and have a sparse hardwood midstory, a moderately dense hardwood midstory that is low in height or a dense hardwood midstory that is low in height are considered "suitable" foraging habitat. "Potentially suitable habitat" includes stands that meet most requirements, but exceed maximum pine basal area/stocking in smaller diameter -at -breast -height (DBH) classes, hardwood midstory density/height and/or overstory hardwood density. These stands have the necessary basal area for 10-inch and larger DBH pines and could meet the SMS with midstory removal, prescribed burning and/or thinning. Stands with suitable overstory characteristics containing a moderately dense or dense midstory that is moderate or tall in height are placed in this category. All stands on sites managed for pine dominance that did not fall into the suitable or potentially suitable categories are classified as "future potential habitat." These stands will require time and management to meet the SMS requirements. RCW foraging habitat (timber stands) separated by more than 200 feet from other foraging habitat was considered non-contiguous and was not counted as available habitat (Service 2003). The acreage for each stand was calculated using ArcGIS software. The resulting acreages were then multiplied by the average number of pine stems per acre for each two-inch diameter class in order to determine the total pine stems >10 inches DBH per stand. The appropriate basal area conversion number was multiplied by the total pine stem count in each two-inch diameter class to get the pine basal area for each two-inch diameter class for each stand. The distribution of foraging habitat within the involved 0.5-mile radius foraging partitions is somewhat fragmented with patches of non -habitat (e.g., roads, fairways, etc.) interspersed among stands of pine and mixed pine -hardwoods. Sufficient acreage of suitable and potentially suitable habitat was not available within 0.25- mile radius inner core foraging partitions and JCA's habitat assessment included the 0.5-mile radii for both RCW groups. Pre -project, SOPI 22-112's 0.5-mile foraging partition contains 3,275.87 square feet (ft) of pine basal area for pine stems > 10 inches DBH on 32.65 acres of suitable habitat, 7,340.63 ft2 on 85.19 acres of potentially suitable habitat and 113.03 ft2 on 4.11 acres of future potential habitat. The project will not require removal of any currently suitable habitat. 2 About 309.53 ft2 of pine basal area for stems > 10 inches on 5.57 acres of potentially suitable habitat will be removed. A 0.5-acre area containing 13.75 ft2 of future potential habitat will be eliminated. Post -project, SOPI 22-112's 0.5-mile radius foraging partition will retain 3,275.87 ft2 of 10+ - inch DBH pine basal area on 32.65 acres of suitable habitat, 7,030.99 ft2 on 79.62 acres of potentially suitable habitat and 99.28 ft2 on 3.61 acres of future potential habitat. The BA states that this partition will meet the SMS requirements post -project assuming potentially suitable habitat is made suitable (USFWS 2003). SOPI 23's 0.5-mile foraging partition contains 2,546.66 ft2 of pine basal area for pine stems > 10 inches DBH on 33.0 acres of suitable habitat, 10,320.82 ft2 on 147.42 acres of potentially suitable habitat and 1,337.9 ft2 on 59.48 acres of future potential habitat. The project will require removal of 47.86 ft2 of pine basal area for stems > 10 inches on 0.83 acre of currently suitable habitat. About 55.91 ft2 of pine basal area for stems > 10 inches on 0.97 acre of potentially suitable habitat will be removed. No acreage identified as future potential habitat will be eliminated. Post -project, SOPI 23's 0.5-mile radius foraging partition will retain 2,498.8 ft2 of 10+ -inch DBH pine basal area on 32.17 acres of suitable habitat, 10,264.92 ft2 on 146.5 acres of potentially suitable habitat and 12,763.72 ft2 on 178.62 acres of future potential habitat. The BA states that SOPI 23's partition will meet the SMS requirements post -project if potentially suitable habitat is made suitable (USFWS 2003). The proposed Knollwood Apartments project is located on the outer edges of the 0.5-mile radius foraging partitions for clusters SOPI 22-112 and SOPI 23. Construction will not involve habitat removal within 0.25-mile of either cluster center, nor within 200 feet of any RCW cavity trees. Sufficient acreage and stocking will remain to allow for both RCW groups to continue to exist. We recommend enhancing the survival of these RCW groups by minimizing impacts to mature pines wherever practicable. Longleaf plantings incorporated into landscaping plans would promote re-establishment of future potential habitat. Based on a review of the information contained in your May 1, 2023 email and Biological Assessment, as well as information available to the Service, we concur with your determination that the proposed construction of the Knollwood Apartments project may affect, but is not likely to adversely affect the RCW. We believe that the requirements of section 7(a)(2) of the Act have been satisfied. We remind you that obligations under section 7 consultation must be reconsidered if. (1) new information reveals impacts of this identified action that may affect listed species or critical habitat in a manner not previously considered; (2) this action is subsequently modified in a manner that was not considered in this review; or, (3) a new species is listed or critical habitat determined that may be affected by the identified action. If you have any questions regarding this matter, please contact Mr. John Hammond at 919-856- 4520 (Ext. 28). Thank you for your continued cooperation with our agency. Sincerely, J O H N Digitally signed by JOHN HAMMOND 023.06.15 15:05:11 H A M M O N D 04'00' for Pete Benjamin Field Supervisor Literature cited: U.S. Fish and Wildlife Service. 2003. Recovery plan for the red -cockaded woodpecker (Picoides borealis): second revision. U.S. Fish and Wildlife Service, Atlanta, GA. 296 pp. 59