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HomeMy WebLinkAbout20090565 Ver 1_Monitoring Plan_20110204DEPARTMENT OF THE ARMY WILMINGTON DISTRICT, CORPS OF ENGINEERS 69 DARLINGTON AVENUE WILMINGTON, NORTH CAROLINA 28403-1343 REPLY TO ATTENTION OF: 1 February 2011 Regulatory Division Action ID No. 2009-00832 Ms. Cyndi Karoly Division of Water Quality NC Department of Environment & Natural Resources 1650 Mail Service Center Raleigh, NC 27699-1650 Dear Ms. Karoly, Dg- oSLPS FEB 0 3 2011 UENR - WATER QUALITY WERMIDS AND STQRMWATER BRANCH This correspondence is in reference to Bachelors Delight Stream and Wetland Mitigation Bank that is being developed by Weyerhaeuser Real Estate Development Company c/o: Mr. Taylor Downing, in coordination with NCSU Natural Resource Foundation c/o: Mr. David Ashcraft, located on the east side of Gum Branch Road (SR 1308), within Bachelors Delight Swamp watershed, north of Jacksonville, Onslow County, North Carolina. The purpose of this letter is to provide you with a final draft of the mitigation banking instrument (MBI) and to request your agency's signature on this document. In addition, we have enclosed a CD copy of the approved October 2010 mitigation plan and survey boundary of the bank property. Pursuant to 60 FR 228, p.58610, 3. Agency Roles and Coordination, "No agency is required to sign a banking instrument; however, in signing a banking instrument, an agency agrees to the terms of that instrument." Please review the attached final version carefully; and if you are in agreement with the terms of the MBI, please sign your appropriate signature block and return it to our office within 30 days of your receipt of this letter. Please note that the mitigation restoration plan, along with an e-mail copy of this MBI, has been provided to the team member of your agency; and that the Wilmington District Office of Counsel has reviewed the property disposition and disposal provisions in the MBI and agrees that these provisions provide adequate preservation assurances for the Bank property. For your information, our review of the instrument has been completed and the Wilmington District Engineer is anticipating signing the mitigation banking instrument upon the 30-day time period. Please note that credits will not be released until items in Section VII of the MBI have been finalized. Thank you again for your time and for your agencies participation in the review of this bank. If you have any questions, please don't hesitate to contact me, at the Wilmington Regulatory Field Office, telephone (910) 251-4811. Sincerely, Mickey Sugg, Project Manager Wilmington Regulatory Field Office Enclosure DISTRIBUTION (with enclosure): Mr. Jim Gregson, Director Division of Coastal Management North Carolina Department of Environment and Natural Resources 400 Commerce Avenue Morehead City, North Carolina 28557-3421 Ms. Jennifer Derby, Chief Wetlands Section - Region IV Water Management Division Environmental Protection Agency 61 Forsyth Street, SW Atlanta, Georgia 30303 Mr. Pete Benjamin U.S. Fish and Wildlife Service Fish and Wildlife Enhancement Post Office Box 33726 Raleigh North Carolina 27636-3726 Ms. Molly Ellwood North Carolina Wildlife Resources Commission 127 Cardinal Drive Extension Wilmington, North Carolina 28405 Ms. Cyndi Karoly Division of Water Quality North Carolina Department of Environment and Natural Resources 1650 Mail Service Center Raleigh, North Carolina 27699-1650 Mr. Pace Wilber National Marine Fisheries Service Habitat Conservation Division Post Office Box 12559 Charleston, South Carolina 29422-2559 Copy Furnished (without enclosure): Mr. Ron Sechler National Marine Fisheries Service Pivers Island Beaufort, North Carolina 28516 Mr. John Dorney Division of Water Quality North Carolina Department of Environment and Natural Resources 1650 Mail Service Center Raleigh, North Carolina 27699-1650 Ms. Becky Fox U.S. Environmental Protection Agency Wetlands Regulatory Section- Region IV 1307 Firefly Road Whittier, North Carolina 28789 Mr. Steve Sollod North Carolina Division of Coastal Management 1638 Mail Service Center Raleigh, North Carolina 27699-1638 Mr. Glenn Catts Hofmann Forest Liaison College of Natural Resources NCSU 2023 Biltmore Hall Raleigh, North Carolina 27695 Mr. Christian Preziosi Land Management Group, Inc. Post Office Box 2522 Wilmington, North Carolina 28402 Mr. Taylor Downey Weyerhaeuser Real Estate Development Company 1412 Eatonton Hwy Suite 700 Madison, Georgia 30850 Mr. David Ashcraft NC State Natural Resources Foundation, Inc. Campus Box 8010 Room 3060, Biltmore Hall Raleigh, North Carolina 27695 (Version June 2009) IN WITNESS WHEREOF, the parties hereto have executed this Agreement entitled "Agreement To Establish Bachelors Delight Stream and Wetland Mitigation Bank in Onslow County, North Carolina": N.C. Division of Water Quality: By: Date: Cyndi Karoly, Branch Chief Wetland and Stormwater Branch 19 (Version June 2009) Attachment CD of Barra II Wetland Mitigation Bank - July 2010 Mitigation Plan 21 BACHELORS DELIGHT STREAM AND WETLAND MITIGATION BANK Onslow County, North Carolina FINAL MITIGATION PLAN Sponsor. Weyerhaeuser Real Estate Development Company 1412 Eatonton Highway, Suite 700 Madison, GA. 30650 Prepared by: AkUMG LAND MANAGEMENT GROUP rmf. Environmental Consultants P.O. Box 2522 Wilmington, N.C. 28402 and. Florence & Hutcheson Consulting Engineers Raleigh, NC October 2010 TABLE OF CONTENTS EXECUTIVE SUMMARY INTRODUCTION ....................... A. Project Overview .................. B. Site Location ........................ C. Watershed Characterization II. MITIGATION GOALS ..................... A. Protect Purpose ......................... B. Geographic Service Area (GSA) III. SITE DESCRIPTION ............................. A. Community Types ............................ B. Vegetation ....................................... C. Soil Characteristics .......................... D. Hydrology/Hydraulic Characteristics IV. STREAM RESTORATION PLAN ............. A. Introduction .......................................... B. Priority I Stream Restoration ............... C. Zero Order Stream Restoration ........... D. Stream Enhancement .......................... E. Stream Preservation ............................ F. Stream and Wetland Buffer .................. V. WETLAND RESTORATION PLAN .......... A. Riparian Wetland Restoration .............. B. Riparian Wetland Enhancement.......... C. Riparian Wetland Preservation ............ D. Non-Riparian Wetland Restoration ...... E. Non-Riparian Wetland Preservation .... F. Reference Wetland/Stream Monitoring VI. BANK IMPLEMENTATION VII. POST-CONSTRUCTION MONITORING ........................ A. Wetland Restoration/Enhancement Success Criteria B. Stream Restoration Success Criteria ......................... C. Stream Enhancement Success Criteria ..................... VIII. SITE MANAGEMENT.......... A. Adaptive Management.... B. Long-Term Management 2 2 2 3 4 4 5 6 6 6 7 7 ..8 ..8 ..9 13 17 21 24 26 26 27 28 29 30 31 32 36 36 39 43 43 43 44 IX. CONCLUSION ................................................................................................................................45 X. SOURCES OF INFORMATION ......................................................................................................46 LIST OF FIGURES, TABLES, AND APPENDICES Figure 1 .................... Figure 2 ................... Figure 3 ................... Figure 4 .................... Figure 5 ................... Figure 6 ................... Figure 7 ................... Figures 7A. thru 7D. Figure 8 .................... Figure 9 ................... Figure 10A. thru 10E ...... Project Vicinity Map USGS Topographic Map ...................................2' LIDAR Topographic Map ................. Geographic Service Area (GSA) Map ...........................Onslow County Soil Survey Map ...............................1998 Aerial Photography Map ........................................... Restoration Plan Map ....................................... Restoration Plan Sheets Typical Plan View and Cross-Section of Wet Ford ................................ Proposed Planting Plan Map ......................................... Monitoring Plan Sheets Table 1. Excluded 14-Digit Hydrologic Units Table 2. Restoration Totals by Stream Reach Table 3. Wetland Mitigation Acreages Table 4. Planting Plan for Small Stream Swamp Community Table 5. Non-Riparian Wetland Planting Plan Table 6. Projected Stream and Wetland Credit Totals Table 6A. Summary of Credits by Mitigation Type Table 7. Project Milestone Schedule Table 8. Proposed Stream Cross-Sections Table 9. Proposed Longitudinal Profiles by Stream Reach Appendix A. Ecoregion Map Appendix B. Approved Jurisdictional Wetland Plat Appendix C. Site Photographs Appendix D. USACE Stream Assessment Data Forms Appendix E. Reference Reach Study/HEC-RAS Modeling Appendix F. Historic Aerial Photography Appendix G. Stream Buffer Effectiveness Correction Factor (SBCF) Maps Appendix H. NCWAM Assessment EXECUTIVE SUMMARY On behalf of the bank Sponsor, Weyerhaeuser Real Estate Development Company (WREDCO), Land Management Group (LMG) is submitting the following comprehensive mitigation plan for the Bachelors Delight Stream and Wetland Mitigation Project. The bank site (approximately 363 acres) encompasses land owned by both WREDCO and The Endowment Fund of North Carolina State University. The site is located near Jacksonville, NC in the headwaters of the New River, a major tributary of the White Oak River Basin (Cataloging Unit 03030001). The project area consists of a network of channelized headwater wetland and stream systems that have been historically altered as a result of silvicultural and agricultural management practices. These practices have compromised the functions of both the wetlands and streams within the project boundaries and degraded water quality in the New River watershed. The goal of the project is to restore the natural hydrologic conditions that existed prior to the initiation of intensive land management in the early 1970s. At the present time, drainage within the headwaters of each of the on-site streams has been modified to artificially increase or decrease the functional size of the surrounding watershed. As a result, channels may become dehydrated due to lack of flow (associated with truncated watersheds) or may experience erosion due to excessive flow velocities (associated with artificially enlarged watersheds). These alterations have been exacerbated by extensive logging within the floodplains and channelization throughout the lower reaches. Stream and wetland restoration activities will involve the backfilling and/or plugging of ditches in the headwaters of each of the reaches and construction of new stream channels where appropriate. The project will also utilize a zero order restoration approach for headwater streams which maintain a natural watershed of approximately 25 to 83 acres. The following restoration plan provides specific information regarding the technical approach for the proposed stream and wetland restoration activities. Information regarding the proposed monitoring procedures and long-term stewardship of the project are also included. 1 I. INTRODUCTION A. Project Overview The Bachelors Delight Stream and Wetland Mitigation Bank site (approximately 363 acres) consists predominantly of channelized headwater wetland and stream systems that have been historically altered as a result of silvicultural and agricultural management practices. The site is located just east of Gum Branch Road, approximately six miles north of Jacksonville, NC, in Onslow County. The site consists of rolling terrain and is bisected by three main stream systems (Hewitts Branch, Huffmans Branch, and Bachelors Delight Swamp). While a majority of the site contains moderately well-drained soils, several areas along the eastern and western sections contain poorly-drained soils associated with interstream divide landscape positions. During the early 1970s, a network of drainage ditches was installed throughout these areas to lower groundwater tables and intercept surface water. Site drainage flows south through the Bachelors Delight Swamp, a third order tributary of the New River - part of the White Oak River Basin (Cataloging Unit 03030001) (DWQ Subbasin 03-05-02). Based upon detailed site investigations, 16,761 If of stream restoration, 5,928 If of stream enhancement and 11,400 If of stream preservation is proposed. A total of 60 ac of riparian wetland habitat has also been targeted for restoration. Non-riparian wetland restoration, located throughout the interstream flats, will comprise approximately 85 ac of the proposed project area. As a result, the restoration effort will allow for increased stream habitat, floodwater storage, nutrient retention/sediment reduction, and intact headwater wetland habitat for resident and migratory fauna. B. Site Location The tract is located east of the junction of Gum Branch Road and Quaker Bridge Road in northern Onslow County, NC (refer to Figure 1). It is bordered on the northeast by the Hofmann Forest. The site is located approximately 6 miles north of Jacksonville. The attached USGS 7.5-minute topographic quadrangle (Jacksonville North quad) depicts the location of the site relative to mapped blue-line streams and canals (Figures 2-3). 2 C. Watershed Characterization The bank site is located within the White Oak River watershed (DWQ Subbasin 03-05-02). The subbasin consists of managed forestry tracts, low-density residential and high density commercial developments along the Gum Branch Road corridor. Population growth within the subbasin is primarily focused in the areas north of Jacksonville and south of Richlands. Streams and waterbodies within the watershed are susceptible to impairment from nutrient loading and low ambient dissolved oxygen (DO) concentrations. According to the White Oak River Basinwide Water Quality Plan (NC DWQ 2005), a majority of the waterbodies within the subbasin are impaired due to nutrient enrichment and periodic fecal coliform bacteria contamination. Surface waters within the project area drain south to Bachelors Delight Swamp, a third order tributary of the New River. The NC DWQ surface water body classification for Bachelors Delight Swamp is C-NSW. Class "C waters are defined as those waters protected for secondary recreation, fishing, wildlife, fish consumption, aquatic life (including propagation), survival and maintenance of biological integrity, and agriculture. Secondary recreation includes wading, boating, and other uses involving human body contact with water where such activities take place in an infrequent, unorganized, or incidental manner. Nutrient Sensitive Waters (NSW) is a supplemental classification intended for waters needing additional nutrient management due to being subject to excessive growth of microscopic or macroscopic vegetation. Best management practices (BMPs), including riparian buffer setbacks, are implemented within NSW basins to help offset or minimize nutrient loading to susceptible waters. The site formerly consisted of several expansive areas of Mesic Pine Flatwood communities dissected by multiple, small stream swamp systems in the headwater areas. Non-riverine headwater wetlands (pocosin and swamp forest), characteristic of the outer Coastal Plain, existed throughout the broad interstream flats in the eastern and western borders of the proposed project area. These type of wetlands support a number of functions/values including, but not limited to the following: groundwater recharge; floodwater storage and attenuation; filtration and storage of nutrients, sediments, and/or toxic substances; and refuge/feeding habitat for resident and migratory fauna. Stream systems work in concert with these wetlands to attenuate flood velocities, provide aquatic habitat, and elevate the surrounding water table. At the present time, these functions have 3 been compromised through silvicultural management and agricultural practices (including ditching, clear-cutting, conversion to fields, agri-chemical runoff, etc.). The New River and its tributaries have exhibited significant water quality impairments associated with low DO, high total nitrogen, and high total phosphorous. High nutrient concentrations originate from non-point source loading associated with intensive agricultural practices common throughout the watershed. These impairments tend to be exacerbated by channelization of streams and ditching of adjacent headwater wetlands, resulting in diminished nutrient uptake and nutrient/sediment loading to down- gradient waters. II. MITIGATION GOALS A. Project Purpose The goal of the proposed bank is to provide high-quality compensatory mitigation for permitted impacts within the White Oak Basin via the restoration, enhancement, and preservation of streams and wetlands. The proposed activities will restore both the hydrologic and vegetative components of four separate stream and wetland communities within the headwaters of Bachelors Delight Swamp. The following categories of functions have been targeted for restoration or enhancement within the Bachelors Delight Stream and Wetland Mitigation Bank: • BIOGEOCHEMICAL CYCLING -The restored stream and headwater wetland systems will capture drainage from the surrounding watershed, dissipating energy in the downstream environment. The increased retention times will allow for a suite of biotic and abiotic processes to convert nitrogen and other nutrients into different forms that may be readily consumed by the surrounding plant community. This retention also allows for sediment to settle out of solution, reducing downstream pollution. Flow within the system will also provide a valuable conduit for organic matter which will support downstream food webs. Cessation of agricultural production within the headwaters will also reduce the nutrient and sediment delivery to downstream waters. • HYDROLOGIC/HYDRAULIC - The watershed restoration approach will provide for the re- establishment of characteristic headwater wetland hydrology and contribute to natural flow 4 regimes for downstream tributaries. Restoration of riparian wetlands and headwater wetland flats will result in the expansion of the surface and subsurface water storage component of the ecosystem. The increase in storage volume will reduce peak discharge, prolong baseflow, and contribute to channel stability. • PLANT and ANIMAL HABITAT- Plantings associated with the various habitats will restore the pine and native hardwood assemblages that existed prior to silvicultural and agricultural management. When coupled with the variation in topography, these areas provide valuable heterogeneity which supports a more diverse food web within the ecosystem. This diversity provides a variety of food sources and refuge habitat for local and migratory species. Increases in plant diversity will also be generated through the development of microhabitats and organic matter inputs to the soil surface. • AQUATIC HABITAT - Restoration of the existing watershed boundaries through the removal of existing drainage ditches will restore natural flow regimes to several reaches within the project area. New channel construction will also create numerous niche habitats through the installation of woody debris, natural pools, etc. Restoration of seasonally driven flow will rehydrate existing channels throughout the headwaters of Hewitts Branch, Huffmans Branch, and Bachelors Delight Swamp. Both methods of restoration will allow for macro-invertebrate and amphibian communities to repopulate these previously inaccessible areas. B. Geographic Service Area (GSA) The tract is located within the Middle Atlantic Coastal Plain (Ecoregion 63) as defined by Griffith et al. (2002) "Ecoregions of North Carolina" (refer to Appendix A). This ecoregion encompasses the area defined as the `Carolina Flatwoods' - a subregion occurring along nearly level, poorly drained areas in the outer Coastal Plain including the White Oak River Basin. The proposed project will serve as a general use wetland and stream mitigation bank serving the White Oak River Basin (USGS Cataloging Unit 03030001). Note that the GSA has been amended based upon comments from the IRT and now excludes the 14-Digit Cataloging Units located to the south and east of HWY 17 in Pender and New Hanover Counties (Figure 4). 5 Table 1 provides a list of the excluded units. Table 1. Excluded 14-Digit HUCs 14-Digit Cataloging Unit 03030001040005 03030001040010 03030001040020 III. SITE DESCRIPTION A. Community Types The tract consists of a variety of former wetland habitat types which coincide with the existing gradients in topography, drainage patterns, and soil types. The primary wetland types targeted for restoration are Coastal Plain small stream swamp and wet pine flatwoods. Based upon the recently developed NC Wetland Assessment Manual (WAM), the targeted community types for the bank site are (1) Non-Riparian Wetland Pine Flat; (2) Non-Riparian Wetland Pocosin; and (3) Riparian Non-Riverine Headwater Wetland. Based upon the Cowardin classification for wetland and deepwater habitats (Cowardin et al. 1979), the wetland community types to be restored are Palustrine Scrub-Shrub and Forested Wetlands (i.e., broad-leaved deciduous, needle-leaved deciduous, needle-leaved evergreen, and broad-leaved evergreen). Changes in restored community types will coincide with changes in topography and soil types across the site. B. Vegetation The predominant land use of the tract and surrounding area is silvicultural (managed pine plantation of various stand stages). Since the tract has been affected by prescribed drainage improvements for forestry production, species indicative of drier, upland conditions are more prevalent in areas currently targeted for riparian restoration and/or enhancement. These species include old field blackberry (Rubus alumnus), dog fennel (Eupatonum capillifolium), bracken fern (Pteridium aquilinum), broom-sedge (Andropogon glomeratus), and loblolly pine (Pins taeda). Non-target species such as sweet gum (Liquidambar styraciflua) and red maple (Acer rubrum) are dominant througout large sections of riparian habitat. More desirable species such as loblolly bay 6 (Gordonia lasianthus), fetterbush (Lyonia lucida), American holly (//ex opaca), red bay (Persea borbonia), and sweet bay (Magnolia virginiana) were observed in isolated areas. Characteristic hardwoods of the small stream swamp community (e.g. black gum, water tupelo, bald cypress) are either sparse or absent in the upper stream reaches targeted for restoration. The species assemblage has clearly shifted in response to long-term site drainage and timber management. C. Soil Characteristics The tract is located within a dissected drainage network and includes broad, flat interstream areas along the perimeter of the project site. Moderately well-drained soils, such as the Goldsboro unit, are found near the intersections of the existing stream channels. These units transition to the somewhat poorly-drained Lynchburg series and to the poorly-drained Rains series, situated in the headwater landscape positions of the existing channels and adjacent to the Hofmann Forest. Bottomland areas associated with the lower portions of Bachelors Delight Swamp are mapped as Muckalee loam, a poorly-drained unit commonly associated with active floodplains throughout the Coastal Plain (refer to Figure 5). D. Hydrology/Hydraulic Characteristics The tract is located within a watershed that has historically received drainage improvements for the purposes of increased timber productivity and/or crop yield (Figure 6). These improvements have resulted in changes to functional watershed size and disrupted natural flow patterns throughout the headwaters of this area. An intensive drainage network exists throughout the 156 ac. of cultivated land in the northeastern portion of the project site. These activities have increased the size of the Bachelors Delight Swamp drainage area while concurrently diverting flow from Huffmans Branch and other tributaries. As a result, these other tributaries exhibit significantly reduced flow and lack evidence of overbank flooding. Evidence of drained hydric soils (i.e. low-chroma, friable soils exhibiting a relatively high percentage of uncoated sand grains) was observed throughout the areas mapped as the Rains soil series. Areas mapped as Goldsboro and Lynchburg have been bedded, but lack a significant network of drainage improvements. These conditions are reflected in the current wetland delineation that received USACE approval in October 2007 (refer to Appendix B). 7 Drainage improvements have also directly impacted streams throughout the lower portions of the watershed. These impacts have increased the cross-sectional area of the natural stream, limiting interaction with the surrounding floodplain and increasing flow velocities during peak flow events. In addition, the straightening and excavation of stream channels has resulted in the removal of large woody debris and other in-stream habitat, reducing biological diversity within the system. Appendix C documents existing conditions throughout each of the main reaches targeted for restoration. IV. STREAM RESTORATION PLAN A. Introduction Like other small, blackwater streams of the Coastal Plain, Bachelors Delight Swamp and its tributaries are susceptible to water quality impairment resulting from non-point source discharges of contaminants - including nitrogen, phosphorous, and a suite of organophosphate-based herbicides and pesticides. Currently, intensive agricultural practices in the headwaters, in addition to concentrated development along the Gum Branch Road corridor, contribute to decreased water quality of downstream waters. Ditches, channelized tributaries, and canals drain an approximate ten-square mile area within the watershed. These surface waters serve as direct conduits for sediment, nutrients, and other pollutants entering both the Bachelors Delight Swamp and the New River. The channelization of streams contributes to channel instability and reduced attenuation on- site. This, in turn, results in increased flooding and bank erosion for down-gradient areas. The natural replenishment of fine sediments and nutrients from floodwaters onto the floodplain wetlands within the site has been virtually eliminated so that sediment accumulation is occurring along the stream bed and nutrients are being shunted downstream. The physical alteration of the stream bed adversely affects biological communities through direct mortality, habitat loss, and shifts in species composition. See Appendix D for additional stream assessment information. 8 Restoration of a natural, sinuous channel will provide the variety of habitat features necessary to support a diverse invertebrate and bacterial community. The re-establishment of these communities increases the uptake of dissolved organic carbon (DOC) within the stream system. As DOC is processed, the microbial loop is established, forming a key component of the food web (Allan, 1995). Restoration of the natural channel will also assist in the maintenance of an elevated water table throughout the adjacent floodplain. Elevation of the water table allows for the reestablishment of hydric soil conditions, which aid in the transformation and sequestration of pollutants. Construction of an appropriate channel pattern and profile will also reduce flow velocities, increase residence time, and promote overbank flooding (resulting in the replenishment of fine sediments and nutrients to adjacent floodplain wetlands). Each of the four stream reaches targeted for restoration exhibit similar geomorphic positions. Thus, it is anticipated that the identified functions to be restored or enhanced are fairly uniform throughout the project area (Figure 7). Table 2 provides specific information for each of the four sections of the project. B. Priority I Stream Restoration The Priority I approach will be applied to reaches that have experienced extensive manipulation to the natural channel and have been disconnected from their natural drainage basins. The physical manipulations to the channels have removed a majority of the in-stream structures and increased the cross-sectional area, resulting in a disconnection from the surrounding floodplain. Disconnection and/or redirection of flows in the headwaters have dehydrated several reaches on the northern side of Maready Road, further compromising the aquatic functions within each stream. Design parameters for this approach were based on the naturally occurring watershed boundaries and corresponding flow characteristics throughout the site. A reference reach was defined near the intersection of BD-2 and BD-3 where a distinct shift from a braided, zero order system to a defined channel was observed. The functional watershed size at this transition point was determined to be 83 acres. This 83 acre threshold was then applied to reaches targeted for 9 restoration throughout the site. Areas containing a post-construction watershed of greater than 83 acres were designed using Priority I techniques, while those maintaining smaller drainage areas incorporated zero-order design elements. Assessments conducted at the reach were also used to determine the dimensionless ratios which determine the final geometry of the Priority I reaches. Table 2. Restoration Totals by Stream Reach Name Restoration Enhancement L2 Preservation Hewitts Branch HE-1 5,103 HE-2 1,900 HE-3 500 HE-4 3,000 Huffmans Branch HU-1 3,445 HU-1A (Zero-Order) 171 1,200 HU-2 (Zero-Order) 1,233 HU-3 2,000 Bachelor's Delight Swamp BD-1/2 (Zero Order) 447 BD-3 1,700 BD-4 (Zero Order) 2,107 BD-4A (Zero Order) 1,274 BD-5 1,728 BD-5A (Zero Order) 949 BD-5B (Zero Order) 0 BD-5C (Zero Order) 0 BD-5D (Zero Order) 0 BD-6 1,700 BD-7 3,600 Half Moon Creek HM-1 (Zero Order) 901 HM-1 1,131 TOTAL 16,761 5,928 11,400 10 Construction of the restored channel will occur directly adjacent to the existing ditch. Spoil material generated from the excavation of the new channel will be used to backfill the existing ditch and restore natural contours within the floodplain. Natural woody material will be used to construct the in-stream structures throughout each section. Hard structures will not be used. Rather, natural materials (such as root wads and log vanes) will assist with channel stabilization and grade control. Hydrologic Modeling: Hydrologic Engineering Center's River Analysis System (HEC-RAS Version 4.0) is a software package designed to perform one-dimensional, steady flow, analysis of water surface profiles for a network of natural and constructed channels. HEC-RAS uses two equations, energy and/or momentum, depending upon the water surface profile. The model is based on the energy equation. The energy losses are evaluated by friction (Manning's equation) and contraction/expansion (coefficient multiplied by the change in velocity head). The momentum equation is used in situations where the water surface profile rapidly varies, such as hydraulic jumps and stream junctions. Backwater analysis was performed for the existing and proposed conditions for both bankfull and 100-year discharges. In addition to steady flow data, geometric data is also required to run HEC- RAS. Geometric data consists of establishing the connectivity of the river system, which includes cross-section data, reach lengths, energy loss coefficients (friction losses, contraction, and expansion losses), and stream junction information. Bankfull Discharge Analysis: HEC-RAS was used to evaluate how the discharge of the restored channel flows within the proposed channel geometry. This evaluation verifies that the proposed plan, dimension, and profile would adequately convey the discharge at the bankfull stage; the point where water begins to overflow onto the floodplain. Bankfull discharge estimates were determined using on-site conditions, the published regional curve, and the mini-regional curve created by Ko/Florence & Hutcheson. 11 Rise/No-Rise Analysis: A HEC-RAS analysis has been prepared and completed on existing and proposed conditions of the project channel(s). The resulting data output has been analyzed to determine if the design channel is adequately conveying its bankfull discharge, and to determine if a rise, fall, or no-rise in water surface elevations during the 100-year flood event has occurred. See Appendix E for specific information from the reference reach and modeling outputs. Hewitts Branch - HE-7: The headwaters of this reach have experienced extensive logging and drainage manipulation since the early 1970s. At the present time, several drainage ditches to the west of and adjacent to Maready Road bisect the natural watershed, reducing flows to the existing channel. Extensive logging within the area has also removed target species and a majority of the mature loblolly pines. As a result, little functional habitat remains throughout this reach. Construction of the single thread channel will involve grading activities designed to re-establish proper elevations and hydrology. The initial grading work will remove existing silvicultural bedding and contour the stream valley corridor to the original grades. Following these activities, each of the ditches within the headwaters of Hewitts Branch will be backfilled to the existing grade, approximately +52' MSL. Removal of a portion of the existing access road will provide source material for the proposed backfilling. Woody debris from recent logging events will be utilized throughout this section to enhance habitat and microtopography within the valley. Approximately 2,000 If of single thread channel will be constructed on the western side of Maready Road. Construction activities for this section will take place within a 400' corridor. A permanent rock ford (see typical on Figure 8) will be constructed at the intersection of Maready Road, replacing an existing culvert. At the present time, the existing culvert maintains an invert elevation similar to the incised channel located downstream. The new culverts will raise the invert elevation to approximately +50' MSL, which will reconnect the stream to the existing floodplain. An additional 3,000 If of channel will be constructed downstream of this intersection. As the valley becomes more defined in this section, the need for contouring will be minimized. Rather, the proposed earthwork will focus on channel construction while repairing logging damage and backfilling of the existing channelized feature. Following these activities, this section will be 12 planted with hardwood species associated with the target small stream swamp community. An estimated total of 5,103 If of restoration, extending from the intersection of the main branch to the zero order tributary, is proposed for this area (Figure 7). Huffman Branch - HU-7: A similar approach will be utilized for this reach, which has been channelized north of Maready Road. Construction work will focus on the backfilling of ditches associated with an access road in the northern section of the project. This will re-establish a drainage connection to a majority of the 110 ac. natural watershed. Installation of new culverts will also be installed at the intersection of existing access road and Maready Road. An estimated total of 3,445 If of restoration, extending north from Maready Road is proposed for this area (Figure 7). Half Moon Creek - HM 7: The headwaters of this reach have been managed for silvicultural production for over 30 years. As a result, extensive channel modification and removal of the characteristic riparian vegetation has occurred throughout the entire reach. Given the level of prior disturbance, the stream corridor will be re-graded to achieve appropriate elevations and contours throughout the existing valley. Backfilling of the existing channel will occur between Maready Road and the southern project boundary. Existing spoil piles and bedding will provide a majority of the source material for this stage of the project. Removal of non-target species such as loblolly pine and sweet gum will occur throughout the 200' wide valley to allow for grading activities to reestablish a gradual transition between riparian and non-riparian habitats. When completed, a functional watershed exceeding 80 acres will provide hydrologic input to downstream section of the reach, restoring up to 1,131 If of first order stream. Note that zero order stream construction will occur upstream of this section providing an additional 901 If of restoration within the headwaters. C. Zero Order Stream Restoration A zero order approach will be applied to the headwater streams associated with the project. The restoration design criteria will be consistent with current publish guidelines for the Coastal Plain (USACE, 2007). Headwater (zero order) streams generally lack a defined bed and bank and are located in smaller watersheds that are typically greater than 25 acres. Prior to developing the site 13 design, several tools were utilized to define the extent of the zero order stream systems within the project area. These tools include 1' contour (LIDAR) data, soil survey data, historic aerial photography, and on-site reference reach surveying. These data were then compared to the proposed post-project watershed size to determine the applicability of the zero order approach. Based on an analysis of the data collected, watersheds between 25 and 83 acres in size are considered suitable for zero order restoration techniques. See Appendix F for historic aerial photography of the site. The length of the valley will be used to determine the final linear footage of zero-order stream restoration. Areas outside of the 100-ft wide corridor (but still within the valley) are targeted for riparian wetland restoration. Plantings consistent with small stream swamp and riparian wetland communities of the outer Coastal Plain will be established as part of the restoration effort. Figure 7 depicts the layout of the stream component of this project. Restoration of the ecosystems will re-establish diffuse, braided flow patterns throughout the identified valley corridor. This will be achieved through removal of existing silvicultural bedding and backfilling and/or plugging of ditches throughout the upper watershed. These activities will allow runoff to sheet flow across the site and access the restored riparian headwater system. The elevation of water table depths will also provide valuable base flow. Huffman Branch - HU- IA: A small section of zero order restoration is proposed directly upstream of HU-1. Proposed construction activities will be identical to those associated with the downstream reach, but will transition into a braided system for approximately 171 If. Modeling indicates that the watershed associated with this section will not support flow within a single thread channel. As a result, this section will transition into a zero order, headwater system. Huffman Branch - HU-2: This reach will be restored through the backfilling and/or grading of the existing ditch network in the headwaters. Ditches along the access road are currently diverting flow from approximately 40 acres to the western tributary (HU-1), resulting in the dehydration of a majority of the reach. Construction activities will restore a hydrologic connection throughout the 60 acre watershed, restoring 2,273 If of zero order stream and associated riparian habitat. 14 Bachelors Delight Swamp - BD2: The drainage connection between the headwaters of this reach and the downstream section of Bachelors Delight Swamp (BD-3) has been severed by the construction of Maready Road. Extensive bedding and logging have also reduced the extent of riparian habitat associated with this reach. Restoration of this section will reestablish a hydrologic connection through the installation of properly sized culverts underneath Maready Road. These features will reestablish the connection to the 60 acre drainage basin, sufficient to provide flow to approximately 447 If of zero order stream. Conditions along the northern side of Maready Road have also deteriorated due to logging practices. Any existing silvicultural bedding will be removed and recontoured to reestablish the natural valley slope. Channelized sections of BD-1 and 2 will also be backfilled to the natural grade. As a result of these activities water tables within the surrounding areas will be elevated, supporting the target riparian community and zero order stream system. Bachelors Delight Swamp - BD-4A: The headwaters of this reach have been managed for agricultural production since the 1970s. As a result, a majority of the hardwood species have been removed and only a limited number of bald cypress saplings remain. Several large collector canals and a network of lateral ditches currently direct flow to the eastern branch of Bachelors Delight Swamp (BD-5). These manipulations have reduced the hydrologic input from the natural watershed significantly and have compromised the aquatic functions of the stream throughout much of the reach. Proposed construction activities will focus on reestablishing the hydrologic connection between the headwaters and the downstream section of this reach. Existing field ditches within the footprint of the proposed zero-order stream will be backfilled and contoured to match the proposed grades of the valley. Backfilling of laterals in the vicinity of the zero-order valley will help restore natural hydrologic inflows (via groundwater contributions and overland flow). The footprint of the proposed zero order system will be based on historic aerial photography (1938) which includes two narrow corridors within the headwaters. Note that a critical component of the headwater restoration will be the backfilling and removal of the collector canal located on the southwestern boundary of the 15 NCSU property. This canal currently dissects the headwater valley and directs flow to the south and east (into the canal that drains to BD-5). Removal of this canal will allow for unimpeded flow from the restored headwater valley to BD-4. Final elevations will be contoured to facilitate drainage into the downstream section of the reach. Following construction activities, a majority of the 80 acre drainage basin will be restored, supporting up to 1,274 If of zero order stream restoration. Bachelors Dg/ ht Swamp - BD-4: The downstream section of this reach has also experienced flow reductions due to the extensive hydrologic modifications within the headwaters. These modifications have effectively removed natural hydrologic input from a majority of the reach resulting direct mortality to the aquatic species. The proposed construction activities associated with BD-4A will restore the natural drainage pathways, rehydrating the existing braided channel system. As indicated above, the boundary canal between WREDCO and NCSU property will be removed and contours graded to match the valley floor. This will provide unimpeded flow from the restored headwaters to BD-4. Additional earthwork associated with BD-4 will be limited to the section directly adjacent to Maready Road. At the present time, the existing culverts are clogged with debris, severing the hydrologic connection to the downstream portion of the reach. As a result, approximately 600-800 If of braided channel has been submerged on the north side of Maready Road. These culverts will be removed and replaced with a permanent rock ford which will facilitate natural drainage to the downstream section of the reach (refer to typical on Figure 8). Combined construction activities for the reach will restore up to 2,107 If of zero order stream habitat. Bachelors De/ yht Swamp - BD-5A: Conditions within the headwaters of this reach are similar to BD-4A. However, due to the existing drainage network constraints from the adjacent tract (Hofmann Forest), the opportunity to restore the entire subbasin is not feasible. As a result, only the western branch has been targeted for zero order stream restoration. Construction within the open fields will remove existing crowns and backfill and/or plug three lateral ditches. The collector canal located on the southwest boundary of the field will also be plugged and backfilled. Final elevations will be contoured to facilitate drainage through the existing wetlands located to the south of the fields. The lower section of BD-5A is also dissected by a forestry road that extends from Maready Road northeast to the boundary of the WREDCO and NCSU properties. Restoration 16 work will include the removal of this spoil road and contouring of the valley to match grades between BD-5A and BD-5. Following completion of all construction activities, the functional drainage area for this reach will exceed the 25 acre minimum threshold and support flow for up to 1,157 If of zero order stream Half Moon Creek - HM IA: This section will connect with the single thread channel construction currently proposed for the downstream section of HM-1. Construction activities will occur on the north side of Maready Road. During this stage of construction the existing culvert will be removed and replaced with a permanent rock ford (refer to Figure 8) to facilitate diffuse flow from the upstream portion of the reach. Work within the headwaters will include backfilling of approximately 2,000 If of existing ditch and recontouring within the 200' wide valley. Following the earthwork phase, all disturbed areas will be planted with a mixture of hardwood species associated with the target small stream swamp community. Based on the existing watershed boundary, up to 901 If of zero order stream will be restored. D. Stream Enhancement The proposed enhancement activities will focus on sections to the south of Maready Road, where direct impacts to the aquatic system are less acute. Stream enhancement will be achieved through a variety of approaches across the site. Overall, management activities have reduced the aquatic functions within several reaches via the alteration of storm-driven hydraulics and removal of in- stream habitat. In addition, the placement of spoil material within the adjacent floodplain compromises stream/floodplain interaction. Hewitts Branch - HE-3: This section, located south of Maready Road, includes approximately 500 If of stream that has been historically impacted by road construction and silvicultural management practices. Areas directly adjacent to the road bed have been channelized and culverted to control runoff and drainage in the vicinity of the constructed road. The existing culvert has not been maintained and flows are currently restricted due to sediment deposition on the upstream and downstream sides. As a result, natural flow is impeded. Channelization has disconnected the stream from the adjacent floodplain. In addition to this 17 disturbance, a large ditch that parallels the entire western edge of the floodplain intercepts surface water and groundwater input to the adjacent stream. Spoil piles from the excavation of the stream currently serve as an artificial boundary to the existing wetlands and divert flow towards HE-1. In addition to compromising stream function, the incised channel adversely affects the hydroperiod of the adjacent riparian wetlands. Overall, management activities have reduced the aquatic functions within this reach via the alteration of storm-driven hydraulics and removal of in-stream habitat. In addition, reduced connectivity of the wetland floodplain reduces the potential for nutrient/pollutant retention. Enhancement of aquatic function will be achieved through the restoration of seasonal variation in flow dynamics via removal of the road bed and the installation of the wet ford. The restoration of a natural flooding regime (amplitude, timing, etc.) will promote the re-establishment of characteristic riparian vegetation. The existing ditch along the western edge of the stream valley will also be filled and restored to the existing grade. Enhancement of riparian wetland hydrology will contribute to stream baseflow (particularly important to stream function during periods of reduced surface water inflow). Based upon the observed conditions, 500 If of Level II Enhancement is proposed for this section. Huffman Branch - HU-3: This section, located south of Maready Road, includes approximately 2,000 If of stream that has been disturbed by road construction and silvicultural management practices. Due to the flow restrictions present along Maready Road, this section drains only a small percentage of its natural watershed. As a result, sections of the channel now resemble braided systems normally associated with headwater wetland areas. Extensive evidence of historic logging within the floodplain was also observed throughout the reach, as indicated by the presence of an expansive clear-cut along the western edge of the existing wetlands. Non-target vegetative assemblages dominated by sweet gum and red maple saplings and trees ranging in age from 10 to 20 years are also present along the eastern section of the floodplain. HU-3 exhibits relative morphological stability along much of its reach. Therefore, enhancement will not require earth work along this section of the tributary. The enhancement of aquatic function will be realized as a result of the reestablishment of natural hydrologic inflows that have been altered 18 by prior land-use practices). Restoration of upstream stream channels (both first order and zero order tributaries) and riparian wetlands will result in functional benefits to downstream waters. The natural hydroperiod of HU-3 has been compromised by prior channelization and compartmentalization of the contributing watershed. These land-use practices have resulted in modifications to channel morphology, floodplain interaction, flow regime, and sediment transport. The combined effects of upstream channelization and compartmentalization via the road bed that bisects the stream reach results in more acute, episodic discharge to HU-3. Characteristic pulsed flooding events will be achieved via the restoration of upstream channels and the removal of an approximate 25-ft wide road bed. A stream valley (wet ford) will be graded within the area of the existing road bed. The existing under-sized culverts will be removed. The eastern ford will reestablish the connection to a 55-acre drainage area associated with HU-2 that is currently serviced by an 18" diameter culvert. The western ford will provide an unrestricted connection to the 300-acre drainage area associated with HU-1 and will expand the natural hydrologic connection to both the restored channel and floodplain associated with the restoration of the HU-1 reach. This connection will support nutrient cycling, invertebrate passage, and reduced flow velocities within the section targeted for enhancement. Approximately 3,300 native hardwoods will also be planted within the adjacent riparian zone to help re-establish the appropriate small stream swamp community. This revegetation within the floodplain will stabilize the areas along the western floodplain that remain sparsely vegetated following the logging activities that occurred in 2007-08. Plantings along the eastern edge will occur in areas currently dominated by non-target species such as red maple and sweet gum. As these plantings mature, they will provide additional shading for the stream channel and refuge habitat for larger fauna. Bachelors De/ yht Swamp - BD-5: This section includes 1,728 If of existing channel located downstream from BD-5A. A majority of this section has been channelized to accommodate drainage from the adjacent forestry operations. Enhancement of aquatic function within this area will be achieved through the removal of the existing soil road and spoil piles located within the floodplain. Following the removal of these features, natural valley contours will be restored to facilitate overland flow into the existing channel. The restored floodplain will serve to filter 19 pollutants and remove sediment, thus improving water quality throughout the reach. An existing conditions HEC-RAS model (models the channel with the culvert) was completed for BD5 which depicts increased water surface elevations for the bankfull, 10 and 100 year storm events when compared with the proposed conditions model (models the channel without the culvert and road bed). The existing and proposed conditions were modeled 500 feet upstream and downstream of the culvert at the soil road to determine the impact on the natural hydrologic regime. The model results show that the culvert has an increase in water surface elevations of 2.58 feet for the bankfull storm, 1.76 feet for the 10 year storm and 1.32 feet for the 100 year storm event when compared with proposed conditions at the inlet of the culvert. These results quantify the extent and frequency of ponding that occurs under the current conditions. Based on these results, removal of the existing culvert will restore natural hydraulics and hydrology within the valley of BD5. These activities will support sediment and debris transport through the system and restore habitat for fauna and flora that has previously been negatively impacted by unnatural inundation. Bachelors De/ipht Swamp - BD-6: BD-6 includes approximately 1,700 If of stream enhancement along its northwestern and southeastern reaches. Functional uplift along BD-6 will be achieved through the reestablishment of a hydrologic connection to restored headwater and riparian wetlands of BD-4, BD-4A, BD-5, and BD-5A. Restoration of upstream zero-order streams, re- connection of natural watersheds, and removal of flow impediments will contribute to the enhancement of stream function throughout BD-6. The reestablishment of a characteristic, pulsed hydrologic regime will promote channel equilibrium, floodplain interaction, and associated nutrient/sediment retention. The southeastern section of BD-6 receives continual, increased inflow from a large borrow pit/pond located immediately east of Maready Road and adjacent to BD-5. A portion of the borrow pit was excavated from the floodplain of BD-5. Flow from BD-5 is re-directed into this pond prior to discharging to BD-6 via a submerged pipe. As a result, the receiving watershed is subject to modified water quality conditions and flow regimes. The altered hydrologic connection between BD-5 and BD-6 also disrupts the passage of semi-aquatic and aquatic fauna between these reaches. Proposed enhancement activities will include the removal of the borrow pit via grading 20 (i.e. infilling) and contouring to pre-disturbance elevations and planting of characteristic riparian vegetation. The outlet pipe underneath Maready Road will be replaced by a large wet ford that will span the natural valley and provide adequate drainage for the upstream watershed. The result will be unimpeded, natural flow to downstream segments. Characteristic hydrologic inflow to the northwestern section of BD-6 will be also be reestablished through the installation of a wet ford at the intersection of Maready Road. While this section exhibits relative morphologic stability, hydrologic input from BD-4 is restricted by a poorly functioning, undersized culvert at the existing road. As a result, flow is not sufficient to maintain proper channel geometry and reduces the frequency and amplitude of overbank flooding of the adjacent riparian wetlands. These conditions persist until the reach connects with the perennial section of Bachelors Delight Swamp (BD-7) (near the confluence of the northwestern and southeastern sections of BD-6). As a result, floodplain benefits (including nutrient exchange/transformation and sediment retention) are compromised along this reach of BD-6. Restoration of the headwater stream and wetlands of BD-4 and BD-4A and the reestablishment of unimpeded flow regimes will promote channel equilibrium and enhanced stream/floodplain interaction. E. Stream Preservation The Bachelors Delight Mitigation Bank site is situated at the headwaters of the New River watershed, immediately north of the more heavily urbanized areas of Jacksonville, NC. Road corridors within the immediate vicinity of the bank site (including Gum Branch Road and Western Boulevard corridors) continue to experience significant residential and commercial expansion associated in large part with the 2005 federal Defense Base Closure and Realignment Commission (BRAC) and resultant population growth. Preservation of headwater streams and wetlands in urbanized watersheds is an important component of maintaining and supporting habitat structure/function and water quality functions of downstream waters (particularly in areas susceptible to near-term perturbations associated with population growth and development). The stream preservation reaches of the Bachelors Delight Mitigation Bank site are situated at the down- gradient terminus of the project. Note that a single-family neighborhood is currently under construction on the parcel directly south of the bank site. Preservation of the streams and 21 wetlands within the lower reaches of the property provides an opportunity to establish a protected corridor from restored upstream areas to down-gradient waters. The White Oak River Basin supports some of the most "biologically significant habitats along the entire U.S. Atlantic Coast" (NCDENR 2007). Habitat conservation within the basin is the focus of the Onslow Bight Conservation Forum, a landscape-scale collaborative conservation effort. One of the major goals of this effort (and as supported by the State of NC) is the buffering of military bases and the protection of natural areas off military lands. The preservation component of the proposed bank site and the connectivity that it would provide to Hoffman Forest is consistent with such goals. It is important to note that the receiving waters of New River support expansive areas of primary nursery area (PNA) and consist of Outstanding Resource Waters (ORW) as defined by 15A NC Administrative Code 031 .0101 and 15A NCAC 02B .0225, respectively. Preservation of contributing stream reaches is important for the continued functioning of these identified coastal resources. Areas of New River south of US Hwy 17 also contain submerged aquatic vegetation (SAV) beds considered Critical Habitat Area under Marine Fishery Council rules. SAV provides important nursery habitat for many species (including blue crabs, penaeid shrimp, and red drum). Predatory fish also utilize SAV habitat for foraging. SAV growth and distribution in particularly is limited by water quality impairments (such as turbidity associated with upstream sediment loading). Restoration and preservation of streams that drain to coastal waters is consistent with the goals and recommendations of the Coastal Habitat Protection Program (CHPP) of the NC Division of Marine Fisheries (DMF). Strategies and recommendations of CHPP include the enhancement and protection of habitats from physical impacts and incentives to reduce non-point source pollution via minimizing losses to wetlands and streams. Preservation of the Bachelors Delight streams is consistent with these strategies. A number of federally-listed species have been identified as occurring within the larger White Oak River Basin. A majority of these species are associated with wetland and aquatic habitats. Listed rare species include the American alligator (Alligator mississippiensis), Croatan crayfish (Procambarus piumimanus), Carolina gopher frog (Rana capito), oak toad (Bufo quercicus), and black swamp snake (Phaiacrocoraxauritus). Of the nearly 100 rare species of vascular plant in the 22 White Oak River Basin, sixty-eight (68) are associated with wetland habitats (NCDENR 2007). Preservation of stream corridors provides functional benefits to the habitats that support these species. Approximately 2 miles of Coastal Plain stream will be preserved in conjunction with the development of the bank site (Figure 7). The areas targeted for preservation range from braided headwater channels to large bottomland hardwood ecosystems. Stream channels within these areas retain the characteristic dimension, plan, and profile relative to their watershed. As a result, the stream/floodplain interaction remains intact and functional. Substantial in-stream habitat, such as overhanging roots mats, snags, and leaf packs also support a diverse invertebrate community within each reach (See Appendix D). In addition, sufficient canopy coverage also exists to regulate stream temperatures during summer months. Hewitts Branch - HE-2: The upper reach of the Hewitts Branch tributary (HE-2), north of Maready Road, has experienced relatively minor silvicultural impacts, and retains a wide, intact wetland community. Preliminary data suggest that this reach would be classified as a DA5 channel. As with most headwater systems, a majority of the flow is directed through a series of braided channels of varying widths and depths. The gentle, sloping topography ranging from +40' MSL to +50' MSL supports a broad floodplain canopy comprised of several native hardwood species. These species include mature water oak (Quercus nigra), swamp chestnut oak (Quercus michauxii), and American holly. Approximately 1,900 If of braided channel have been proposed for preservation in this reach. The adjacent riparian wetlands have also been targeted for preservation based upon the native hardwood assemblage composition and lack of silvicultural disturbance. Hewitts Branch - HE-4: The remaining length of Hewitts Branch, south of the intersection of HE-1, has been targeted for preservation. The section includes approximately 3,500 If of a high quality second order stream that has experienced minimal impact from the surrounding silvicultural management activities. Data indicate that this reach would be classified as a C5 channel. A distinct valley is present throughout the lower reaches of the branch with elevations ranging from 23 +30' MSL to +45' MSL. The floodplain is comprised of a natural assemblage of native hardwoods such as black gum, swamp chestnut oak, and water oak. Approximately 400' of intact floodplain are present throughout this area. Huffman Branch - HU-IA: This section, located to the north of HU-1, contains approximately 1,200 If of small, zero order stream channel. The canopy is comprised of a natural assemblage of native species such as black gum, red bay, and wax myrtle (More//a cerifera). While existing trees and shrubs indicate logging within the last 10 to 20 years, the stream appears to be stable and functional. Preservation of the reach as part of the bank project will ensure long-term protection of the reach and its associated functions. Bachelors Delight Swamp - BD-3: This section, located downstream of BD-1/2, has been targeted for preservation. Located on the south side of Maready Road, this section includes approximately 1,700 If of high quality first order stream that maintains a relatively stable channel and associated floodplain. Approximately 150' of intact floodplain are present throughout this area with a well- defined valley that ranges from +32' to +46' MSL. The floodplain is comprised of a natural assemblage of native species such as black gum, red bay, and water oak. Bachelors Qg/ ht Swamp - BD-7: The remaining section of Bachelors Delight Swamp encompasses approximately 3,600 If of high quality second-order stream that has been minimally impacted by the adjacent logging operations (Figure 7). A distinct valley is present throughout this section with elevations ranging from +28' MSL to +46' MSL. The floodplain is comprised of a natural assemblage of native hardwoods such as black gum, swamp chestnut oak, and water oak and would be categorized as a bottomland hardwood ecosystem. Approximately 800' of intact floodplain are present throughout this area. F. Stream and Wetland Buffer Per the 2008 Mitigation Rule, compensatory mitigation may include "the protection and maintenance of terrestrial resources, such as non-wetland riparian areas and uplands, when these resources contribute to or improve the overall ecological functioning of aquatic resources in the watershed" (CFR 332.3(c)(2)). In addition, the North Carolina IRT recently released a draft of the 24 'Regulatory Guidance for the Calculation of Stream and Buffer Mitigation Credit for Buffer Widths Different from Standard Minimum Widths NC (Version 4.57 Draft)': The purpose of the guidance is to provide a mechanism by which stream mitigation credits may be adjusted (upward or downward) when proposed stream buffers differ from the standard, minimum width (i.e. 50 feet in piedmont and coastal plain streams). Within the guidance, specific criteria are identified for the application of the stream buffer effectiveness correction factor (SBCF). Providing additional buffer width (in excess of 50 feet) will result in a corresponding increase in stream mitigation credit. The proposed buffer widths for Bachelor's Delight Mitigation Bank are a minimum of 151 ft (corresponding to a 13% increase in stream credit). The actual area of uplands along each reach is variable depending upon the width of the valley corridor to be restored, enhance, or preserved. The entire width of the buffer area (both within existing valley corridors and within adjacent uplands) will be protected via the conservation easement deed to be recorded for the site. Appendix G provides additional information on specific stream reach totals based upon the application of the SBCF. The proposed buffer area is also depicted in Figure 7. Upland buffer areas that have been recently clear-cut (outside of existing valleys) will be restored via the planting of longleaf pine (Pins palustris). Based upon project design, approximately 129 acres of upland buffer will be restored and protected in perpetuity via the conservation easement deed. Of this acreage, approximately 35 acres are associated with first order streams and thus are incorporated into the SBCF calculations. The upland buffer areas exhibit moderately well-drained to well-drained sandy soils (Goldsboro and Norfolk series). The upland restoration effort is intended to restore the Atlantic Mesic Longleaf Woodland community (Peet and Allard, 1993) that existed prior to anthropogenic disturbances., In addition to longleaf pine, this community includes southern red oak (Quercus falcata), post oak (Quercus stellata), and water oak. A diverse herbaceous layer may also develop if fire suppression is minimized. Restoration of this diverse community offers an excellent opportunity to restore conditions that existed in the late 19th century. In light of the effort to restore and preserve this upland community type in adjacent uplands, a more favorable ratio for wetland preservation is requested (see below). 25 V. WETLAND RESTORATION PLAN A. Riparian Wetland Restoration Approximately 60 acres associated with the degraded stream systems have been targeted for restoration. As discussed in the previous section, these areas have been converted to monoculture pine plantations through silvicultural management activities over the past four decades. A majority of the targeted areas are located in the transitional zone between the managed pine stands and the remaining jurisdictional wetlands. The vegetation within these areas is comprised of red maple, sweet gum, and red bay saplings. Table 3 provides specific information on the proposed acreages for each wetland type included within the bank site. Hydrologic Restoration: Characteristic hydrology of riparian areas will be restored through the reestablishment of natural drainage basins and channel design throughout the site. The proposed channel work will raise the bed elevation, minimizing subsurface drainage and increasing overbank flooding within the adjacent floodplain. Restoration of the natural watershed boundaries throughout the upstream sections will also increase the effective drainage basin size, which will provide additional hydrologic input. The proposed restoration footprint for these areas was generated through the use of HEC-RAS modeling, 1' contour LIDAR data, geomorphic data, and observed field conditions. For example, the existing jurisdictional wetlands associated with HU-1 are found along the +42' MSL contour. Output from the HEC-RAS modeling projects a flood elevation of 46' during a 1 Year storm event. This suggests that sufficient hydrologic input from a relatively small rain event will result in overbank flooding within the valley following stream restoration activities. These overbank events coupled with the surface inflow of the restored watershed and the elevation of groundwater levels will re-establish characteristic hydrology of the riparian wetlands. Vegetative Restoration: The proposed restoration areas will be planted with species typical of a small stream swamp community (Figure 9). Plantings will include bald cypress (Taxodium distichum), swamp tupelo (Nyssa biflora), ironwood (Carpinus caroiiniana), and swamp chestnut oak. Trees will be planted on 9-ft spacings, corresponding to 538 trees per acre. It is expected that other characteristic species will recruit naturally into these restored areas upon successful hydrologic restoration. 26 Table 3. Wetland Mitigation Acreages Type Proposed Acreage Riparian Restoration 60 Riparian Enhancement 28 Riparian Wetland Preservation 48 Non-Riparian Restoration 85 Non-Riparian Preservation 13 SBCF/Upland Buffer 129 TOTAL 363 Table 4 provides more information regarding species quantities and composition for the small stream swamp community. Table 4. Planting Plan for Small Stream Swamp Community Small Stream Swamp 60 ac. Riparian Restoration Common Name Scientific Name % Composition # Planted Bald Cypress Taxodium distichum 30 9,684 Swamp Tupelo Nyssa biflora 25 8,070 Red Bay Persea borbonia 20 6,456 River Birch Betula nigra 15 4,842 Ironwood Carpinus caroliniana 10 3,228 TOTAL 32,280 B. Riparian Wetland Enhancement Approximately 28 acres of existing jurisdictional wetlands have been targeted for enhancement. At the present time, these areas are located along narrow fringes adjacent to the degraded stream systems. Characteristic vegetation has been altered through silvicultural management activities that included clear-cutting, bedding, and ditching. While these areas technically meet the criteria for jurisdictional wetlands, excavation and maintenance within the existing channels has 27 compromised the natural hydroperiod. As a result, flooding duration and frequency has been reduced. Existing wetlands that have been degraded by prior channel excavation will be enhanced via stream restoration. Elevation of the channel bed and reconnection of the stream to the adjacent floodplain will re-establish characteristic riparian wetland hydrology. Any areas in which vegetation is removed as part of the stream restoration effort will be replanted with characteristic riparian wetland species. As a result of the stream restoration, a natural hydrologic regime and habitat assemblage will replace the current degraded system. These activities will contribute to additional biogeochemical cycling and habitat utilization throughout the existing jurisdictional wetland footprint. C. Riparian Wetland Preservation Approximately 48 acres of habitat located along the existing stream reaches has not been adversely impacted by prior site management activities exhibit relatively natural wetland conditions. As such, these areas will remain intact and functional via incorporation into the conservation easement. This area was examined using the methodology outlined in NCWAM User Manual and data sheets are provided in Appendix H. A relatively mature canopy comprised of native species (e.g. swamp tupelo and bald cypress) and characteristic sub-canopy species (e.g. ironwood, American holly, and red bay) was observed throughout the lower reaches of Hewitts Branch, Huffmans Branch, and Bachelors Delight Swamp. These areas were characterized by natural hummocks and microtopographic lows capable of retaining 6 to 12 inches of water following inundation. All floodplains associated with these areas provide ample substrate for sediment and pollutant retention during high flow events and reduce downstream flow velocities. Protection of these corridors will also provide valuable habitat connectivity to the vast protected headwater wetlands of the adjoining Hofmann Forest. Given the relatively undisturbed condition of these riparian wetlands, calculated NC WAM rating, and the incorporation of upland buffers across the entire bank site (see Section III (F) above), a 5:1 ratio is proposed for the riparian wetland preservation. 28 D. Non-Riparian Wetland Restoration Approximately 85 acres within the project boundary have been targeted for non-riparian wetland restoration (Figure 7). This area has been actively cultivated for several decades for the production of soybeans, cotton, and other commodity crops. As part of the conversion to agricultural fields, an extensive network of ditches and canals was installed to improve drainage. A majority of the soils are mapped as Pantego loam, a very poorly drained series commonly associated with shallow depressional areas and broad, interstream flats in the Coastal Plain. Spacing between the laterals ranges between 330' and 350'. Lateral ditches range in depth from 3'-4', and the larger collector canals range from 5'-7'. Hydrologic Restoration: Restoration of the 85 acres of non-riparian wetland habitat will be achieved via the backfilling and/or plugging of ditches. In addition, removal of the collector canals along the southern boundary of the fields will allow for surface water to sheetflow into the restore stream channels. Installation of ditch plugs and associated grading work along secondary and tertiary ditches will restore characteristic wetland hydrology to the streamhead pocosin and wet pine flat habitats (refer to Figure 9). Doing so will restore natural groundwater hydroperiods and provide for increased surface storage. Vegetation Restoration: Following construction activities the area will be planted with characteristic wetland species coinciding with gradients in landscape position and anticipated hydrologic conditions (Figure 9). Plantings will be designed to transition from the small stream swamp community to a fringe of streamhead pocosin. The streamhead pocosin, located on the outer valley fringe, will be characterized by a higher density of pond pine concurrent with a decrease in abundance of bald cypress and black gum. Areas of slightly higher topography occurring within interstream flats will be planted with increased abundance of pond pine. The shrub layer will be comprised of American holly and loblolly bay. Other characteristic shrub species (e.g. inkberry, fetterbush, American titi) will likely volunteer into the area due to the proximity to Hofmann Forest. Tree seedlings will be planted on 9-ft spacings (equivalent to a density of 538 stems/acre). Shrub species will be planted on 8-ft spacings (equivalent to a density of 680 stems per acre). Table 5 provides additional information on species and quantities. 29 Functional Restoration: Restored wetlands will intercept runoff from adjacent crop fields, dissipate stormwater velocity, and enhance nutrient and sediment trapping. These restored functions are likely to have discernible benefits to water quality and habitat downstream. Vegetative restoration will provide for increased foraging and refuge habitat for resident and migratory species. In light of acute development pressures in this region of eastern North Carolina, the White Oak River Basin is particularly susceptible to loss of wetland functions and associated watershed impacts. By providing for successful restoration of an expansive non-riparian wetland system, the Bachelors Delight Wetland and Stream Mitigation Bank will help to replace wetland functions critical to water quality and wildlife habitat in the area. Table 5. Non-Riparian Wetland Planting Plan Streamhead Pocosin 9 ac. Non-Riparian Restoration Common Name Scientific Name % Composition # Planted Swamp Tupelo Nyssa biflora 25 1,345 Bald Cypress Taxodium distichum 20 1,076 Pond Pine Pinus serotina 20 1,076 Atlantic White Cedar Chamaecyparis thyoides 15 807 Tulip Poplar Liriodendron tulipifera 15 807 Sweetbay Magnolia virginiana 10 538 TOTAL 5,649 Wet Pine Flat 76 ac. Non-Riparian Restoration Common Name Scientific Name % Composition # Planted Pond Pine Pinus serotina 40 30,558 Sweetbay Magnolia virginiana 15 11,459 Red Bay Persea borbonia 15 11,459 Inkberry Ilex glabra 15 11,459 Huckleberry Gaylussacia frondosa 15 11,459 TOTAL 76,396 GRAND TOTAL 82,045 E. Non-Riparian Wetland Preservation Approximately 13 acres of non-riparian wetlands, located within the headwaters of HU-1, will be 30 included within the conservation easement. This area was also rated based on the methodology described in the NC WAM User Manual which evaluates the overall functions of the system (Appendix H). Although this block has been managed for silvicultural production, extensive ditching and/or bedding has been limited to the perimeter of the block. As a result, subsurface storage has not been significantly impacted, allowing hydrologic input from the block to provide baseflow for the zero order and first order sections of Huffmans Branch. Ample opportunity for surface storage, in the form of microtopographic variation within the block was also observed. This variability modulates peak flow during large rain events which limits the potential for erosion within the restored channel. Vegetation within the block has been managed for loblolly pine production but the assemblage does include native hardwoods that have remained undisturbed for 20 years. The assemblage includes mature loblolly pine, black gum, red maple, and loblolly bay in the canopy and sub-canopy strata. Understory species include red bay, American titi, high-bush blueberry, fetterbush, and inkberry. Herbaceous and woody vine species include netted chain fern, Virginia chain fern, royal fern, and greenbrier. The diverse assemblage is characteristic of relatively undisturbed non-riparian wetland flats in eastern North Carolina. The relative maturity of the stand will provide valuable refuge habitat and serve as a corridor for migratory wildlife between the Hofmann Forest and the surrounding bank site. In light of the functions (both water quality and habitat) supported by this intact wetland assemblage, a 7:1 ratio is proposed for this section of preservation. F. Reference Wetiand/Stream Monitoring LMG has identified multiple reference areas within the existing wetland stream communities within the property. The preservation areas of Hewitts Branch (HE-2) contain a stable, intact stream system and adjacent riparian community. This feature will likely serve as a reference for both zero order stream and riparian wetland habitat, as no alterations to the existing watershed are proposed for this section. The lower reach of Hewitts Branch (HE-4) contains a single thread channel stream and a small stream swamp/bottomland hardwood community suitable for use as a reference area. Hydrologic monitoring equipment will be installed in these two areas 90 days prior to initiation of construction activities. An array of three monitoring wells (WM-40s) will be installed across the existing valley at each of the two locations. These gauges will record water table depths within the 31 riparian wetlands and water depth within the stream channel on a daily basis. The calibration point of the in-stream well will correspond to the bankfull elevation of the stream channel. As a result, positive readings (calculated above the calibration point) will provide evidence of overbank flooding. These data will then be compared to those from the adjacent riparian wetlands to develop a regression analysis that correlates rainfall to stream discharge. Similar monitoring techniques will be applied to those areas targeted for restoration and enhancement in order to determine the success of the proposed design. VI. BANK IMPLEMENTATION The Bank Sponsor (WREDCO) will enter into a binding agreement with The Endowment Fund of North Carolina State University to implement the proposed bank. Together, these entities own fee simple title for the entire bank site. The Sponsor and The Endowment have control of all ditches affecting groundwater hydrology of the site. Since the restoration is premised on re-establishment of groundwater hydrology via removal of ditches, all water rights necessary for sustainability of the bank are secured through the fee simple ownership. Upon execution of the MBI, a conservation easement deed for The Endowment Fund acreage will be conveyed to the NC State Natural Resources Foundation (Foundation) (a 501 (c)3 entity). Both Weyerhaeuser (WEYCO) and the Foundation have demonstrated experience in mitigation site implementation and habitat restoration. WEYCO has conducted previous wetland restoration projects in sites in Louisiana and is routinely engaged in reforestation and habitat restoration projects. Thus, the Sponsor is well-versed in site restoration techniques, reforestation practices, and site management. In addition, the Foundation is an integral part of the land grant mission of NC State University. As a result, it is responsible for the procurement and management of tracts of land throughout North Carolina. The Foundation is also responsible for the operation and management of the Hofmann Forest Bank located immediately adjacent to the proposed Bachelors Delight Bank. Design and monitoring expertise is provided by LMG and Ko-Florence Hutcheson (stream designer). Both LMG and Ko have designed and implemented numerous large-scale restoration projects for full-delivery (EEP and NCDOT) and project-specific permit mitigation. 32 Many of the site evaluations (e.g. soil profile descriptions, hydrologic monitoring and modeling, and vegetative surveys) have been completed for the site. One reach (BD-5) continues to be monitored in the event a viable restoration design can be developed. If data support a viable restoration approach, then the design for this reach will be submitted prior to plan approval. The Mitigation Banking Instrument (MBI) will also be submitted during the plan review. Upon acceptance of the final mitigation plan by the IRT and execution of the MBI by all parties, the Bank Sponsor will record a conservation easement deed for the site and will initiate proposed construction activities. Mitigation bank credits will be calculated using the following standard: Mitigation Type Ratio (1) Wetland Restoration 1:1 (2) Wetland Enhancement 2:1 (3) Wetland Preservation (Riparian) 5:1 (4) Wetland Preservation (Non-riparian) 7:1 (5) Stream Restoration 1:1 (6) Stream Enhancement (Level II) 1.5:1 (7) Stream Preservation 2.5:1 In addition, the SBCF will be incorporated for determination of the total stream credits. Table 6 provides a summary of the credits for both the stream and wetland components of the bank site. Table 6A provides a breakdown of quantities (acreage/linear feet) and credits by mitigation type. Use of credits from the Bank to offset wetland and stream impacts authorized by federal permits or state water quality certifications must be in compliance with the Clean Water Act, Section 404 (b)(1) guidelines and other applicable federal and state legislation, regulations, and policies. Prior to release of bank credits, the following requirements will be met: (1) approval of the final mitigation plan and execution of the MBI; (2) recordation of the conservation easement deed; and (3) establishment of appropriate financial assurances. Given the aforementioned ratios for wetland and stream restoration, it is estimated that 249 wetland restoration equivalent credits and 26,507 stream credits will be derived from the establishment of the Bachelors Delight Wetland and Stream Mitigation Bank. 33 Table 6. Projected Stream and Wetland Credit Totals Streams (linear feet) Priority 1 Zero Order Enhancement Type Restoration Restoration (Level 11) Preservation SBCF Hewitts Branch 5,103 500 4,900 656 Huffmans Branch 3,445 1,404 2,000 1,200 431 Bachelors Delight Swamp 4,777 3,428 5,300 Half Moon Creek 1,131 901 147 TOTAL 9,679 7,082 5,928 11,400 1,234 CREDITS 9,679 7,082 3,952 4,560 1,234 GRAND TOTAL 26,507 Wetlands (acres) Proposed Type Acreage Credits* Riparian Restoration 60 60r Riparian Enhancement 28 14re Riparian Wetland Preservation 48 1Ore Non-Riparian Restoration 85 85r Non-Riparian Preservation 13 2re Stream/Upland Buffer 129 0 TOTAL 363 171 *r = restoration credit; re = restoration=equivalent credit (refer to page 33 for ratios) Table 6A. Summary of Credits by Mitigation Type Mitigation Type Credits Stream 26,507* Riparian (Non-Riverine) Wetland 84 Non-Riparian Wetland 87 *Includes credits derived from SBCF The tentative schedule for establishment of the bank site is outlined in Table 7. Upon execution of the MBI, a conservation easement deed for the site will be conveyed to the NC State Natural Resources Foundation (a 501 (c) 3 entity). The terms and conditions of the conservation easement will ensure the protection of the site in perpetuity. The ownership of the Bank will reside with the Sponsor until completion of the debiting of the Bank. The Foundation will 34 Table 7. Project Milestone Schedule Task Project Milestone Projected Completion 1 Approval of Mitigation Plan and Execution of MBI December 2010/Januar 2011 2 Recordation of Conservation Easement Deed February 2011 3 Initiation of Site Earthwork March 2011 4 Mitigation Site Earthwork Completed September 15, 2011 5 Mitigation Site Planting and Installation of Monitoring Devices January 15 through February 15, 2012 6 Submittal of As-Built Report May 2012 7 First Year Annual Monitoring October 2012 8 Submittal of Monitoring Report #1 to IRT February 15, 2013 9 Submittal of Monitoring Report #2 to IRT February 15, 2014 10 Submittal of Monitoring Report #3 to IRT February 15, 2015 11 Submittal of Monitoring Report #4 to IRT February 15, 2016 12 Submittal of Monitoring Report #5 to IRT February 15, 2017 13 Submittal of Monitoring Report #6 to IRT February 15, 2018 14 Submittal of Monitoring Report #7 to IRT February 15, 2019 15 IRT Close-out Meeting March 2020 be responsible for long-term protection and management of the site. The easement prohibits any activities (e.g. timbering, farming, building, etc.) that would alter the environmental state of the Bank site. The Bank Sponsor will be responsible for securing appropriate financial assurances in the form of construction, monitoring, and maintenance bonds to cover contingency measures in the event of Bank default or failure. Performance monitoring will be conducted for a 7-year period subsequent to project construction. Annual monitoring will evaluate the development of wetland function and document site performance relative to established success criteria. In addition, monitoring activities will identify any site deficiencies that may warrant remedial action. Monitoring reports documenting site success and/or failure will be submitted to the IRT each year. Upon submittal of annual monitoring reports demonstrating the fulfillment of site success criteria, stream and wetland credits will be released according the approved credit release schedule. The Sponsor shall develop accounting procedures for maintaining accurate records of debits made from the Bank that is acceptable to the IRT. Such procedures shall include the generation 35 of a debit report by the sponsor documenting all credits used at the time they are debited from the bank. Debit reports shall be provided to each member of the IRT within 30 days of the date of credit sale. In addition, the sponsor shall prepare an Annual Report to be provided to each IRT member within thirty (30) days of each anniversary of the date of execution of the MBI, showing all credits used and the balance of credits remaining. The sponsor's reporting obligations hereunder shall end upon the sale of all credits or termination of the MBI, whichever event first occurs. VII. POST-CONSTRUCTION MONITORING A. Wetland Restoration/Enhancement Success Criteria The wetland restoration effort will be evaluated based upon performance criteria related to vegetative density and wetland hydrology. Monitoring will be conducted at the site an annual basis for a period of seven (7) years. Note that non-planted individuals of characteristic wetland species may volunteer into the restored site. Suitable volunteers are an important component to the restored wetland as they serve as indicators for appropriate hydrologic regimes and provide increased diversity. The presence of suitable volunteers demonstrates trending of the site toward vegetative success. The primary success criteria for the Bachelors Delight Wetland and Stream Mitigation Bank will be: 7. Demonstrated density of planted species to meet or exceed 320 trees per acre at the end of three years (post-planting), 260 trees per acre at the end of five years, and 270 (seven-year old) character canopy tree species per acre at the end of seven years. The lRT may allow for the counting of acceptable volunteer species toward the 270-1ree per acre density upon the review and evaluation of the annual monitoring data. 2. If within the first three years, any species exhibits greater than 50% mortality, the species will either be re planted or an acceptable replacement species will be planted in its place. 3. No single volunteer species (most notably red maple, loblolly pine, and sweet gum) will comprise more than 50% of the total composition at Year 2 or Year 3. If this occurs, remedial action, as 36 approved by the lRT may be required. During Year 4 and Year 5, no single volunteer species, comprising over 50% of the total composition, may be more than twice the height of the planted trees. if this occurs, remedial action, as approved by the lRT may be required. The need to conduct additional volunteer sampling after Year 5 will be determined by the lRT 4. The hydrologic criterion is premised on the specific community type to be restored. (a) For the non-riparian wetland pine flat, the hydrologic criterion will be the establishment of a static water table at, or within, 72" of the soil surface for 6% of the growing season, equivalent to 78 days based upon hydrologic monitoring undertaken from 07Feb through 30N6 v of each monitoring year. On 07Feb, soil temperature at three of the monitoring plots will be measured at 72 inches below the soil surface and documented within the monitoring report. Should earlier monitoring be considered, the project sponsor must also document biological activity on the site pursuant to the applicable Regional Supplement to the 7987 Wetland Delineation Manual Earlier monitoring must be approved by the U.S. Army Corps of Engineers prior to commencement. (b) For the non-riparian pocosin, the hydrologic criterion will be the establishment of a static water table at, or within, 72" of the soil surface for 10% of the growing season, equivalent to 30 days based upon hydrologic monitoring undertaken from 07Feb through 30N6 v of each monitoring year. On 07Feb, soil temperature at three of the monitoring plots will be measured at 72 inches below the soil surface and documented within the monitoring report. Should earlier monitoring be considered, the project sponsor must also document biological activity on the site pursuant to the applicable Regional Supplement to the 7987 Wetland Delineation Manual. Earlier monitoring must be approved by the U.S. Army Corps of Engineers prior to commencement. (c) For the small stream swamp (headwater riparian) community (zero-order geomorphic position), the hydrologic criterion will be the establishment of a static water table at, or within, 72" of the soil surface for 12.5% of the growing season, equivalent to 38 days based upon hydrologic monitoring undertaken from 07Feb through 30N6 v of each monitoring year. On 07Feb, soil temperature at three of the monitoring plots will be measured at 72 inches below the soil surface and documented within the monitoring report. Should earlier monitoring be considered, the project sponsor must also document biological activity on the site pursuant to the 37 applicable Regional Supplement to the 7987 Wetland Delineation Manual. Earlier monitoring must be approved by the U.S. Army Corps of Engineers prior to commencement. Vegetation Monitoring: The vegetation monitoring protocol is adapted from the accepted methods used for wetland restoration sites within North Carolina. Given the size of the project, 2% of the planted wetland areas will be monitored via the establishment of permanent 0.10-acre plots. These areas include approximately 145 acres in three different habitat types (Figure 10A-10E). Given the proposed acreage, a total of 29 plots will be established. GPS coordinates for the centers of each sampling plot will be recorded and included with the `as-built' survey and subsequent annual monitoring reports. During monitoring, surviving planted individuals and volunteer individuals will be identified and enumerated within each plot. Hydrology Monitoring: Shallow groundwater hydrology will be monitored via seven automated wells (RDS, Inc. WM-20s) located within the non-riparian restoration areas (Figure 10A-10E). Additional wells (10) will be installed in perpendicular arrays within the riparian zone of the first order and zero-order stream corridors. Wells will be installed in accordance with installation methods outlined in the Wetlands Regulatory Assistance Program (WRAP) Technical Note 00-02 (Sprecher, 2000). Water levels will be recorded once daily. Data will be downloaded from the wells every three months (i.e. once quarterly). Data from well downloads will be compiled and graphically displayed to demonstrate hydroperiods of monitored areas. The data will be analyzed in the context of the antecedent rainfall conditions which will also be displayed on well hydrographs. Annual monitoring reports will provide quantitative data of vegetative success, qualitative observations, and conclusions pertaining to mitigation site development. In addition, comparative hydrographs of the restoration areas and corresponding reference areas will be provided. Monitoring reports will be submitted to the IRT no later than February 15th of the following year. Note that the Year 4 and Year 6 monitoring reports will contain only qualitative data regarding the condition of the restored stream reaches. 38 B. Stream Restoration Success Criteria The primary success criteria for the First Order Stream systems will be: Documentation of 2 bankfull events using techniques discussed below within a normal rainfall year in 3 of the 5 years of monitoring. Additional monitoring maybe necessary in the event of abnormal climatic conditions. The primary success criteria for the Zero Order/Headwater Stream systems will be Documentation of2 flow events using techniques discussed below within a normal rainfall year in 3 of the 5 years of monitoring. Additional monitoring may be necessary in the event of abnormal climatic conditions. Level 1 Monitoring will be required for the stream portion of the Bachelors Delight Wetland and Stream Mitigation Bank as detailed in the Stream Mitigation Guidelines, April 2003. Monitoring will occur every year for the five year monitoring period. Monitoring reports will be prepared each monitoring year and will include completed Channel Mitigation Monitoring Sheets with current data, a discussion of any deviations, and whether they are indicative of a stabilizing or destabilizing situation. Level 1 Monitoring includes the following: (7) Photo-Documentation Extensive photo documentation is proposed for the stream monitoring phase of this project. Photos will be taken at all permanent cross-sections on a bi-annual basis (winter and summer) in addition to any problem areas that may develop after construction is completed. Photos will be georeferenced to the corresponding cross-section and/or problem area as part of the submitted report. Photo documentation will also be used to document the health of the riparian area plantings and the effectiveness of any erosion control measures. 39 (2) Ecological Function The health of the riparian vegetation will be documented as part of the wetland restoration monitoring efforts. Multiple 0.10 ac. permanent monitoring plots will be established throughout the riparian wetland restoration including areas directly adjacent to the restored channel. The success criteria for wetland restoration is provided in Part A of Section V. (3) Channel Stability/Survey Procedures a. Cross-Sections (First Order Channel) The Bachelors Delight Wetland and Stream Mitigation Bank will restore 9,679 If of first order Coastal Plain stream. The restoration will mimic low gradient, low velocity stream reaches characteristic of the outer Coastal Plain. No hardened materials (i.e. rock structures) will be used. Rather, natural materials (such as root wads and log vanes) will assist with channel stabilization and grade control. Given the size, uniform design, and gentle slope (0.005) of the proposed project, cross-sections will be established every 1,000 feet of stream length (totaling 12 permanent stations). Placement of these stations will be designed to assess the performance of potential problem areas (e.g. severe erosion, structural failure, etc.). These stations will also be evenly distributed between riffles and pools throughout the project. Table 8 lists the number of cross- sections to be monitored for each reach. Refer to Figure 10A-10E for proposed placement of cross-section monitoring stations. Table 8. Proposed Stream Cross-Sections. Reach Name Proposed I Cross-sections Hewitts Branch (HE-1) 5,103 6 Huffmans Branch (HU-1) 3,445 4 Half Moon Creek HM-1 1,131 2 Total 9,679 12 b. Longitudinal Profiles (First Order Channel) Guidelines regarding longitudinal profiles for projects totaling over 3,000 If suggest that 30% of the area be surveyed on an annual basis. Based on this guideline, a total of 4,850 If of profile would 40 be required for the Bachelors Delight project. The 4,850 If of survey will be divided throughout the individual reaches and will include the permanent cross-sections (Table 9). Data presented in the annual monitoring reports will be shown in comparison to as-built conditions. c. Stream Flow Monitoring (First Order Channel) Documentation of stream flow within the project will also be conducted. Following stream construction activities, six (6) stream gauges (two in each first order channel) will be installed (Figure 10A-10E). Three additional gauges will also be installed throughout the areas targeted for enhancement. These gauges will measure the elevation of water in the channel on a daily basis and will be used to determine the cross-sectional area of the channel under a variety of flow conditions. Table 9. Proaosed Lonaitudinal Profiles by Stream Reach Reach Name Proposed (If) % of Project Profile (If) Hewitts Branch HE-1 5,103 53 1,500 Huffmans Branch (HU-1) 3,445 21 1,000 Half Moon Creek (HM-1) 1,131 7 500 9,679 3,000 In addition to these data, velocity measurements will be collected within 24 hours of a 0.5, 1.0, and 2.0 inch rain event at each gauge location during Year 1 monitoring. Measurements will be collected at 1-foot intervals across the restored channel at depths of 0.5 ft. above the bottom. This information will be used to compute a total discharge measured in cubic feet per second for each reach for the duration of the monitoring activities. All data will then be used to develop a regression analysis which will define the relationship between rainfall events and total stream discharge. These data will be presented in graphical format with individual bankfull and high flow events highlighted. 41 d. Stream Flow Monitoring (Zero Order/Headwater) While the monitoring protocol for restored first order streams is well established, flow documentation within zero-order stream systems is the topic of on-going research throughout the Coastal Plain. Both qualitative and quantitative information will be used to document the occurrence of flow within the proposed restored zero-order stream valley. Quantitative data will be collected using automated shallow groundwater monitoring wells installed in perpendicular arrays across the valley to assist in identification of riparian wetlands and to increase the density of data points for analysis of hydrographs up and across the valley. Arrays will be approximately 1,000 feet apart (along the long axis) for each valley. The center well in each array will be in the lowest part of the valley and the number of wells in the array will be dependent upon width and slope of each valley. Data collected from these wells will then be correlated with elevation data from the longitudinal profiles to infer flow. Open channel flow monitoring equipment may be used to calculate specific flow velocities and duration in each of the five restored reaches. Site visits will also be conducted following rain events to document the upstream extent of observed flow within each reach. GPS data will be collected to mark this location. These data in addition to the flow monitoring data will also be used to calibrate a regression analysis which will establish a relationship between rain event size and stream flow. This analysis will then be extrapolated to future rain events to highlight the number of flow events on an annual basis. Qualitative data will be collected during the on-site investigations to document surface water flow. This shall be accomplished using photographic evidence of observed flow coupled with a preponderance of field indicators of recent flow events in the form of a natural line impressed on the bank; shelving; changes in soil characteristics; destruction of terrestrial vegetation; presence of litter and debris; wracking; vegetation matted down, bent or absent; sediment sorting; leaf litter disturbed or washed away; scour; deposition; bed and bank formation; water staining; or change in plant community. All field indicators present will be documented in each monitoring report. All quantitative and qualitative data will be used to document the upstream limit of flow, which will provide the basis for length of successful zero order stream restoration (i.e. valley length). 42 While published research supports the restoration of streams with similarly sized watersheds in eastern North Carolina, inconsistencies in design or construction may result in non-compliance with the approved mitigation plan. If insufficient flow is observed during the course of post-construction monitoring the total number of stream credits may be reduced to reflect the extent of documented flow or converted to wetland credit per the review and approval of the IRT. Prior to any changes in the amount of available credit, a formal review of the available data would be requested by the Bank Sponsor. C. Stream Enhancement Success Criteria The primary success criterion for the First Order Stream Enhancement will be: Documentation of increases in flow duration and frequency compared to pre-construction conditions during periods of normal rainfall. As discussed in the previous sections, a majority of the stream enhancement will occur through the reestablishment of interconnectivity with the upstream portions of the watershed. This reestablishment will increase the functional acreage of the watershed, corresponding to increased flow frequency and duration in the lower sections of each stream. In order to determine the extent of flow enhancement, a total of three gauges (one per reach) will be installed 90 days prior to construction (Figure 10A-10E) within enhancement reaches HE-3, HU-3, and BD-6. Recorded data will be combined with cross-sectional survey information to determine pre-construction discharge levels. These data will serve as the baseline for the remainder of the project. VIII. SITE MANAGEMENT A. Adaptive Management The Bachelors Delight Stream and Wetland Mitigation Bank is planned and designed to be self- sustaining over time, but some active management or maintenance may be necessary to ensure the long term sustainability of the mitigation efforts. The adaptive management approach involves analysis of monitoring results to identify potential problems occurring on the site and the 43 identification and implementation of measures to rectify those problems. Remedial actions may include, but are not limited to, mechanized earth work (e.g. adjustment to the invert elevations of earthen plugs) or supplemental planting in the event areas do not meet vegetative success criteria. Prior to initiating any remedial actions the proposed measures will be submitted to the IRT for review and approval. Performance and functioning of the mitigation site may be affected by various causative factors, both natural and anthropogenic. Natural hazards may include invasive species and/or excessive herbivory. Human errors may include design flaws, construction deviation, and/or inadequate planting coverage. To minimize these potential problems, the following strategies may be employed: 1. If herbivory appears to be jeopardizing the survivorship of planted species, discussions with appropriate agencies will be initiated to determine an appropriate course of action. 2. Beavers will be trapped from the tract if significant damage appears to be caused by beaver activity. 3. Construction errors will be identified as early as possible via the as-built report. If it appears as those potential errors jeopardize the integrity of the project, appropriate remedial action will be identified and submitted to the USACE for concurrence prior to implementation. 4. Planting errors in spacing density or coverage will be minimized by careful coordination with planting crews. An account of planted stems will be provided with the as-built report. 5. If monitoring indicated a potential design flaw, remediation options will be reviewed. 6. In the event groundwater monitoring wells are damaged by bears, barb-wire fencing and/or other acceptable deterrents may be used to protect wells from further damage. B. Long-Term Management The mitigation approach and establishment of mitigation site boundaries has been designed to minimize long term management issues. As a result, the potential for hydrologic and boundary conflicts have been minimized. The Sponsor has identified the NC State Natural Resources 44 Foundation, Inc. (a 501 (c)3 entity of North Carolina State University) as a potential grantee of the conservation easement deed. The recorded conservation easement deed will ensure the protection of the project in perpetuity. IX. CONCLUSION The establishment, use, and operation of the Bachelors Delight Stream and Wetland Mitigation Bank will provide a quality compensatory mitigation alternative for authorized wetland impacts occurring within the White Oak River Basin. The bank will be established and operating in advance of development impacts in the area. Therefore, its use will help to reduce uncertainty in the CWA Section 404 permit program by having established compensatory mitigation credit available to applicants. In addition, the Bank will more effectively replace wetland and stream functions within the watershed through consolidation of design, implementation, monitoring, and management of mitigation activities (Fed. Reg., 1995). Based upon the current USACE jurisdictional determination and detailed site investigations, over 25,000 If of stream and 246 acres of wetlands have been degraded by historical land-use activities (including ditch excavation and clearing for timber production). The proposed bank will provide for a watershed-level restoration approach for the headwater complex of the Bachelors Delight Stream. Through the implementation of the proposed mitigation activities and the placement of a protective real estate mechanism (i.e. conservation easement), degraded habitats and associated functions will be restored. Together with the adjacent protected lands of Hofmann Forest, the project will provide water quality and habitat benefits on a watershed and regional level. 45 X. SOURCES OF INFORMATION Allan, J.D. 1995. Stream Ecology: Structure and Function of Running Waters. Chapman and Hall. London. Cowardin, L.M., et. al. 1979. Classification of Wetlands and Deepwater Habitats of the United States. US Fish and Wildlife Service. Washington, D.C. Mitsch, W.J. and J.G. Gosselink. 1993. Wetlands (Second Edition). Van Nostrand Reinhold, New York. NC Department of Environment and Natural Resources (DENR). 2007. May 2007 White Oak River Basinwide Water Quality Plan. North Carolina Division of Water Quality. 2001. Watershed Restoration Plan for the White Oak River Basin. Raleigh, NC. North Carolina Division of Water Quality. 2006. Standard Operating Procedures for Benthic Macroinvertebrates. Raleigh, NC. N.C. Wetland Functional Assessment Team. 2007. N.C. Wetland Assessment Method (NC WAM), Draft User Manual. 183 pp. Peet, R.K. and D.J. Allard. 1993. Longleaf Pine Vegetation of the Southern Atlantic and Eastern Gulf Coast Regions: A Preliminary Classification. Proceedings of the Tall Timbers Fire Ecology Conference. No. 18. Tallahassee, Fl. pp. 45-81. Schafale, M.P. and A.S. Weakely. 1990. Classification of the Natural Communities of North Carolina. Third approximation. N.C. Natural Heritage Program, Raleigh, N.C. Skaggs, R.W. et al. 1995. Reference Simulations for Evaluating Wetland Hydrology, in Campbell, K. (ed.), Versatility of Wetlands in the Agricultural Landscape. American Society of Agricultural Engineers, pp. 1-10. U.S. Army Corps of Engineers, U.S. Environmental Protection Agency, Natural Resources Conservation Service, U.S. Fish and Wildlife Service, and National Marine Fisheries Service. 1995. Federal Guidance for the Establishment, Use and Operation of Mitigation Banks; Notice. Vol. 60, No. 228. 10pp. 46 FIGURES Map source: Nortn Garouna Atlas & Gazetteer. Ng 77.2uus Bachelors Delight Mitigation Bank LMG Figure 1. Onslow County, NC q I) Vicinity Map 01_09_168 ? Ln vi: cri rnrnt,N Co+uultcr[, 't7? ???fp??? gym. Q sp. r ?yy ?Yy? 'v1+ r$?'''. ` ?yG"r `?''tit? Y) % X44^ q? v ?°? 4 #?''??.? q ?• >?, " <? ?a.? ?, ? ?a aid '" r` ? r l I 0 1,200 2,400 3,600 Feet Bachelors Delight Swamp Mitigation Bank Onslow County Figure 3. 2ft. LIDAR Contour Map LMG LAND MANAGEMENT GEOOP - Environmental Consultants N Figure 4. Bachelors Delight Mitigation Bank Geographic Service Area Map Onslow County, NC GG 4 8 Miles December 2009 LAND Environmental Consultants Gatp? 55 4 y c "? Ili s s ?r f - 1 ?-, W H I T E 0 A K P 0 C s H O F M A N N F i ?. zh ?' gRAPF - I qA, p0A0 l w *Boundaries are approximate and are not meant to be absolute. Map Source: Jacksonville NW Quadrangle 7.5 minute (topographic) 1990. SCALE 1" = 3,000' Bachelors Delight Mitigation Bank LMG Figure 2. Onslow County, NC NIANA,L,111,',I (,xtaI'I,,,,. USGS Topographic Map 01-09-168 `°II.. (Jacksonville NW Quad) *Boundaries are approximate and are not meant to be absolute. Map Source: NRCS Soils Map. Bachelors Delight Mitigation Bank Onslow County, NC 01-09-168 LMG C 1 c;xuzT,- Lnv lr in nlen F,T I COnSn font, SCALE 1" = 1,000' Figure 5. NRCS Soil Survey I J R+ a'?._ ? 4 9 t ? f 'n Ir Y + Ir. ? ??C. } 1 ... k 4 ..G •YyM ed' ? ?-; •?•. _. ? •1 ;1.gb 4 '^a'l it Y , *Boundaries are approximate and are not meant to be absolute. Map Source: 1998 NAPP aerial photography Bachelors Delight Mitigation Bank Onslow County, NC 01-09-168 LMG LAYI) NIANAGEN'IE:N'r GROUP iu Ln vfron.r?rt'nra! Consultants SCALE 1" = 1,000' Figure 6. 1998 Aerial Photography HE-2 Wet Ford/ HE-1 HE-4 rl Legend (NOTE: Acreage And Distances Provided Are For Complete Project) Property Boundary Existing Roads Stream Restoration (9,679 It) Stream Enhancement (-5,928 It) Zero Order Restoration (7,082 If) Stream Preservation (-11,400 If) Riparian Wetland Restoration (60 ac.) Non-Riparian Wetland Restoration (-85 ac.) o 0 0 o 0 Riparian Wetland Enhancement (-28 ac.) Riparian Wetland Preservation (-48 ac.) Non-Riparian Wetland Preservation (-13 ac.) Stream Buffer (SBCF)(-35 ac.) Upland Buffer (94 ac.) _:1WETLANDS@009 WETLANDS FILESl01-09-168 --- Onslow 19 Batchelors, DowneydACADIOctober 20101FIg7-RestorationPlan-( BD-1 HU-2 Wet Ford BD-3 Wet Ford BD-7 BD-2 BD-4 6-0 00 00000 0„0„0 Wet Ford s:! BD-5 D-5 Ford Wet Ford HM-1 Slreem Design Provided by. Ka/Flonance S Hutcheson 5121 Kingdom Way, Suite 190 Raleigh, NC 27607 919-851-6066 0 300 600 1,200 2,400 0001011 Project: Dale: LMG Bachelors Delight Swamp 12117/2008 1. Nil C'dSAWEU M raor,, Stream and Wetland Mitigation Bank Scale: Title: 1'=1200' Post Office Box 2522 Site Design Dia m By: Wilmington, North Carolina 28402 CBM Telephone: 910-452-0001 Revision Dab: 9115110 Job Number 01-08352 Sheet Number Figure 7 s HE-2 Wet Ford d Wet Ford HE-7rr e, HE-3 Legend (NOTE: Acreage And Distances Provided Are For Complete Project) Property Boundary Existing Roads Stream Restoration (9,679 I? Stream Enhancement (-5,928 If) Zero Order Restoration (7,082 10 Stream Preservation (-11,400 10 Riparian Wetland Restoration (60 ac.) Non-Riparian Wetland Restoration (-85 ac.) o 0 0 o 0 Riparian Wetland Enhancement (28 ac.) Riparian Wetland Preservation (-48 ac.) Non-Riparian Wetland Preservation (-13 ac.) Stream Buffer (SBCF)(-35 ac.) Upland Buffer (-94 ac.) L:\WETLANDS\2009 WETLANDS FILES\01-09-168 --- Onslow 19 Batchelors. Downev\ACAD\October 2010\Fia7-RestorationPlan-C HE-4 steam Design Provided by: KolFlonnce & Hutcheson 0 250 COO 1,000 5121 Kingdom Way, Suite 100 J J Raleigh, NC 27807 919-851-8088 Project: Date: Revision Date: LM G Bachelors Delight Swamp St d W tl d Miti ti B k 12117/2009 9/15/10 ream an e an ga on an Scale: Job Number 1"=500' 01 08 352 Title: - - Post Office Box 2522 Site Design Drawn By: Sheet Number Wilmington, North Carolina 28402 cBM Figure 7A Telephone: 910-452-0001 t2010.dwa '7 Y<1 > HU-2 HU-1 / ' Ford H Legend (NOTE: Acreage And Distances Provided Are For Complete Project) Property Boundary Existing Roads b _ Stream Restoration (9,679 If) 1 Stream Enhancement (5,928 If) Zero Order Restoration (7,082 If) Stream Preservation (11,400 ID Riparian Wetland Restoration (60 ac.) Non-Riparian Wetland Restoration (-85 ac.) 0 0 0 0 0 Riparian Wetland Enhancement (-28 ac.) Riparian Wetland Preservation (-48 ac.) 0 250 500 1,000 Non-Riparian Wetland Preservation (-13 ac.) Project: Date: Bachelors Delight Swamp 12117/2009 Stream Buffer (SBCF)(~35 ac.) LMG Stream and Wetland Mitigation Bank Scale: Title: 1"=500' Post Office Box 2522 Site Design Drawn By: Upland Buffer (-94 ac.) Wilmington, North Carolina 28402 CBM Telephone: 910-452-0001 L:\WETLANDS\2009 WETLANDS FILES\01-09-168 --- Onslow 19 Batchelors. Downev\ACAD\October 2010\Fio7-RestorationPlan-Oct2010.dwo Steam Design Provided by: Ko/Flonnce & Hutcheson 5121 Kingdom Way, Suite 100 Raleigh, NC 27807 919-851-8088 Revision Date: 9115/10 Job Number. 01-08-352 Sheet Number Figure 7B "0" "0`?0 0 00 0 0 0 C, 0 ,..• 0 7 00 0 0 p° 0 00 O O?C? J BD-2 `? J 0 0000 BD-1 00000 0 0 0 0 00 ` Wet Ford 0 eF Wet For i BD 0 BD-3 ?4. l rC. BD-5 Wet Ford BD-5B Wet Ford Legend (NOTE: Acreage And Distances Provided Are For Complete Project) - BD-6 BD 5C ?- Property Boundary W & ? Existing Roads Stream Restoration (-9,679 It) BD -7 BD-5D ??,• ??-,, Stream Enhancement (5,928 It) Zero Order Restoration (7,08210 r Wet Ford Stream Preservation (11,40010 Riparian Wetland Restoration (60 ac.) Non-Riparian Wetland Restoration (-85 ac.) 0 0 0 0 0 Riparian Wetland Enhancement (-28 ac.) 7277277. stream Design Prodded Ill KelFlonmce 6 Hutcheson Riparian Wetland Preservation (-48 ac.) 0 250 500 1,000 5121 Kingdom Way, suits lob 0001101 Raleigh, NC 27607 9, Non-Riparian Wetland Preservation (-13 ac.) 985,A066 Project: Date: Revision Dale: Bachelors Delight Swamp 1211712009 9/15110 Stream Buffer (SBCF)(35 aC.)GI IF3 rx, lrv stream and Wetland Mitigation Bank Scale Job Number. ` 1"=500' 01-08352 Title: Post Office Box 2522 Site Design Drawn ay sheet Number Upland Buffer (94 ac.) Wilmington, North Carolina 29402 CBM Figure 7C Telephone: 910452-0001 L:IWETLANDSP2009 WETLANDS FILESW1-09-168 -- Onslow 19 Bacchelors, DowneylACADIOCtOtber 20101Fig7-RestomtionPlan-Ocl2010.dwg IRF IRF _ IRF Legend (NOTE: Acreage And Distances Provided Are For Complete Project) Property Boundary Existing Roads Stream Restoration (9,679 If) Stream Enhancement (5,928 If) Zero Order Restoration (7,082 If) Stream Preservation (11,400 If) Riparian Wetland Restoration (60 ac.) Non-Riparian Wetland Restoration (-85 ac.) o 0 0 o 0 Riparian Wetland Enhancement (-28 ac.) ; Riparian Wetland Preservation (-48 ac.) Non-Riparian Wetland Preservation (-13 ac.) Stream Buffer (SBCF)(-35 ac.) Upland Buffer (-94 ac.) .:METLANDSP2009 WETLANDS FILESW1-09-168 -- Onslow 19 Bacchelors, Downey\ACADIOctober 20101Fig7-RestorationPlan-C 7 PF 0 150 300 600 1111111111111111101 Project: Date: L1Y117 Bachelors Delight Swamp 1211772009 LM G Stream and Wetland Mitigation Bank r:: • Scale: 1"=300 Title: Post Office Box 2522 Site Design Dram By Wilmington, North Carolina 28402 CBM Telephone: 910-052-0001 Slnan Design Provided by: KofFlunnee S Hutcheson 5121 Kingdom Way, Suite 100 Raleigh, NC 27607 919851-6066 Revision Date: 9115110 Job Number. 01-09352 Sheet Number Figure 7D Wet Ford HM-1 PERMANENT FORD CROSSING SCALE: NTS WATER DIVERSION CHANNEL (2' WIDE x 6" DI PLAN VIEW MIN BANKFULL TO 5 FT 1 10' OUT J MIN BANKFULL WIDTH_ 1 5 FT BANKFULL TO 10' OUT BANKFULL WIDTH FILTER FABRIC WATER DIVERSION J BANKFULL CHANNEL DEPTH (2' WIDE x 6" DEEP) CROSS-SECTION CLASS A RIP RAP/ NATIVE GRAVEL/COBBLE MIN DEPTH 8 " COMPACTED/ROLLED Bachelors Delight Stream and Wetland Mitigation Bank FIGURE 8. TYPICAL PLAN VIEW AND CROSS-SECTION OF PERMANENT FORD CROSSING Final Mitigation Plan - October 2010 (Note: Typical drawing provided by Florence & Hutcheson Consulting Engineers) lv? ? ??1q:u.,, __ W... ?e :' . i •. ? arc M. HE-2 HE-3 HE-1 r,..i HE-4 F Legend Property Boundary ?JV Existing Roads "rb Small Stream Swamp (-60 ac.) Streamhead Pocosin (-9 ac.)?"? Wet Pine Flat (-76 ac.) 0 0 Supplemental Plantings ?i Existing Wetlands (-89 ac.) L:METLANDS12009 WETLANDS FILESW1-09-168 -- Onslow 19 Batchelors, DowneyWCADIOctober 20101Fig9-PlantingPlan-OctO HU-1 "t BD-112 HU-2 , BD-3 HU-3 BD-7 -o C. BD-4A BD-4 BD-5 BD-6 BD-5C BD-5D 1 ,t 1 A iL , . A 1, JI. 10, . r. to, ei 0 300 600 1,200 2,400 HM-1 LLG Past Office Box 2522 Imington, North Carolina 28402 Telephone: 910-452-0001 I 1 i ?I 1 , yr??. t s? "? herd '? at: Date: Bachelors Delight Swamp 1/612010 m and Wetland Mitigation Bank Scale: 1"=1,200' Planting Plan Drawn By: CBM Revision Date: NA Job Number 01-09-168 Sheet Number Figure 9. Legend (NOTE: Acreage And Distances Provided Are For Complete Project) Property Boundary Existing Roads Stream Restoration (9,679 If) Stream Enhancement (5,92810 Zero Order Restoration (7,082 If) Stream Preservation (-11,40010 Riparian Wetland Restoration (-60 ac.) Wetland Enhancement (-28 ac.) J Riparian Wetland Preservation (-48 ac.) Stream Buffer (SBCF)(-35 ac.) Upland Buffer (94 ac.) Monitoring Plot Monitoring Well Stream Gauge • Stream Cross-Section Longitudinal Profile Zero-Order Well Array _:1WETLANDS@009 WETLANDS FILES101-09-168 -- Onslow 19 Batchelors, DowneyWCADIOctober 20101Fig10-MonitaringPlan-( 0 50 100 200 400 '-K LMG Po?un VaSM1p1A%1' i?xncs ou,Dour-, W Cu.,?el,mrc, Post Office Box 2522 Wilmington, North Carolina 28402 Telephone: 910-452-0001 a `=1 rt: Dale. Bachelors Delight Swamp 115/2010 in and Wetland Mitigation Bank Scale: 1"= 200' Monitoring Plan Drawn By: CBM Stwom Design Pmvided by: KolFlorence a Hutcheson 5121 Krgoom Way, Suite 100 Raleigh, NC 27607 919-851-6066 Reyision Date: 9/21110 Job Number 01-09-168 Sheet Number Figure 10A Legend (NOTE: Acreage And Distances Provided Are For Complete Project) Property Boundary Existing Roads Stream Restoration (9,679 ID Stream Enhancement (5,92810 Zero Order Restoration (7,082 ID Stream Preservation (-11,40010 Riparian Wetland Restoration (-60 ac.) Wetland Enhancement (-28 ac.) Riparian Wetland Preservation (-48 ac.) Stream Buffer (SBCF)(-35 ac.) Upland Buffer (94 ac.) Monitoring Plot Monitoring Well Stream Gauge • Stream Cross-Section Longitudinal Profile Zero-Order WeII Array _:1WETLANDS@009 WETLANDS FILES101-09-168 -- Onslow 19 Batchelors, DowneyWCADIOctober 20101Fig10-MonitaringPlan-1 0 50 100 200 400 LMG N FMFNT GRMI w Post Office Box 2522 Wilmington, North Carolina 28402 Telephone: 910-452-0001 0t: Dale. Bachelors Delight Swamp 11512010 m and Wetland Mitigation Bank Scale: 1"= 200' Monitoring Plan Drawn By: CBM Stream Design Provided by: Ill t Hutcheson 5121 Gngdom Way, Suite 100 Raleigh, NC 27607 919-851-6066 Reyision Date: 8127110 Job Number 01-09-168 Sheet Number Figure 10B 1 1, 1. 1' • ,? 1 1 1 1 1 1 1 1 1 1 1 1 11 1 1 1 1 11 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 11 1 11 11 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 11 1 1 1 1 11 11 11 11 1 1 11 1 11 1 1 11 1 1 1 1 11 11 11 111111 111 1 1 ' 1 1 11 1 1 1 1 1 1 1 1 u,. 1 .\? 1 1 11 ` 1 11 11 1 11 1 1 11 1 11 1 1 1 1 1 1 11 1 1 1 1 1 1 y ... 1 1 11 1 11 11 1 1 1 .. .... 1 1 1 1 1 1 ... ..... 1 1 1 1 1 1.. ..y 1 1 11 1 1 1 1 1 1 11 1 1 1 °•. .. + 1 1 1" 1 1 i -?' •... W \ Legend (NOTE: Acreage And Distances Provided Are For Complete Project) . " Property Boundary Existing Roads Stream Restoration (-9,679 If) Stream Enhancement (5,928 If) Zero Order Restoration (-7,082 ID Stream Preservation (-11,400 It) Monitoring Plot Riparian Wetland Restoration (-60 ac.) Monitoring Well Wetland Enhancement (-28 ac.) !_J F_J F_J F_ Stream Gauge • Riparian Wetland Preservation (-48 ac.) ® Stream Cross-Section Project: Data: Bachelors Delight Swamp 1/512010 LMG Stream Buffer (SBCF)(-35 ac.) Strom and Wetland Mitigation an ItMln ? u anr' Srale: Longitudinal Profile _ , Title: Upland Buffer (94ac.) 0 50 100 200 400 Post Office Box2522 Monitoring Plan Drawn By: Zero-Order Well Array Wilmington, North Carolina 28402 CBM Telephone: 910-452-0001 _:1WETLANDS@009 WETLANDS FILES101-09-168--Onslow 19 Batchelors, DowneyWCADIOctober20101Fig10-Monita ingPlan-October2010.dwg 1 d Shea. Design P-1ded by: Ko/Flomnce & Hutcheson 5121 Kngdom Way, Suite 100 Raleigh, NC 27607 919-851-6066 Revision Date: 9/21/10 Job Number 61-09-168 Sheet Number Figure 10C Legend (NOTE: Acreage And Distances Provided Are For Co P t B d roper y oun ary Existing Roads R ti 679 If St t 9 ream ora on ( ) es , Stream Enhancement (5,928 If) Zero Order Restoration (7,082 If) Stream Preservation (11,400 ID Riparian Wetland Restoration (-60 ac.) - Wetland Enhancement (-28 ac.) Riparian Wetland Preservation (-48 ac.) Stream Buffer (SBCF)(-35 ac.) Upland Buffer (-94 ac.) Monitoring Plot Monitoring Well Stream Gauge • Stream Cross-Section Longitudinal Profile Zero-Order Well Array .:1WETLANDS%2009 WETLANDS FILES101-09-168-- 0 50 100 200 400 0001011 Sheen Design Provided by: So/Florence 6 Hutcheson 5121 pngdom Way, Suite 100 Raleigh NC 27607 919-851-6066 94 - Led (NOTE: Acreage And Di Property Boundary For Complete Project) Existing Roads Stream Restoration (-9,679 ID Stream Enhancement (5,928 If) Zero Order Restoration (-7,082 ID Stream Preservation (-11,400 ID Riparian Wetland Restoration (-60 ac.) Wetland Enhancement (-28 ac.) Riparian Wetland Preservation (-48 ac.) Stream Buffer (SBCF)(-35 ac.) Upland Buffer (94 ac.) Monitoring Plot Monitoring Well Stream Gauge • Stream Cross-Section Longitudinal Profile Zero-Order WeII Array :1WETLANDS%2009 WETLANDS FILES101-09-168-- x o°n°o°o°o°o°o o?ooooo00000 o°o°o° °o°o°o 000 o°o°o°o°o°o°o 00000 000000 0 0 0? o 0 0 0 0 C76? o 0 o°o°o°o°o?Oo oho°0°0°o°o°o 0 0 0 0 oho°o°o o°o°o°C 0 000 0 000 00 - o0 o _ c 0 CO00 0 000000 - ?0 0 0 0 'A_ r1 .Am '49 0 125 250 500 1,000 LMG r. psi., ?ianncr.?rrM`r cioutr ?, Post Office Box 2522 Wilmington, North Carolina 28402 Telephone: 910-452-0001 Dt Dale: Revision Date: Bachelors Delight Swamp 111202009 9/21/10 m and Wetland Mitigation Bank Soale: Job Number 1"=500' 01-09-168 Monitoring Plan Drawn 6y: Sheet Number DBM Figure 10E APPENDIX A. ECOREGION MAP Ecoregions of North Carolina 84° 83° 82° 81° 80° 79° 78° 77° 76° 5 ;_ --? ---- ?- 66 - ---- -- 63 ?-a3n' T - --? 45 - ? 63 €63c 'ZA 66c i --'-----------'-f-- _--_-- - - -----' -- 6 t k - /??? 66m -- --- ,- e y63d 63 166 1( i' 5 3b ?. ,. .. 6i Boone C? 65m63e _ 66V Winst ?? v `...? ?'. 45f 63 45 o ? ? 36 e?s g 66< 'j OGreensboro,, T)urha +Knoxville ,?,,?•_ ?? o? r l l ?_i 66d+ % 661 + o T r r 66 )? ¢66 ? 6 i? (1 66 45g ?Mc&, Itnu 5 63n - ? Raleigh P --? 6'Ca, 36° e C 63 1 J 66 6' evi X661 45b 45c C?een 3 63b / lc ' e 4 63e 66g 45 ?. 45f 65m? L J ?? y?fi3g ' e66d " 45i O b6 66d ?? ?•? - ?- - - ---- -. Charlott? 65c 5 S TE ()63b 63g 35° Fayett i e? - -? - - - 66 ?Sg + + r r? w Greenville 45 ? 3 66 j r - - - - 63h N 63h q`.-- 651 ) 45 f'T .651) ..,? 65p` 63nn v 1C J? - - - ?'- 65 ??,-•\/ _ Wilmington 34° r .\_A, _ 63h + + Athens' J 63 V 340 Myrtle Beach 0 84° 830 820 81 80 79° 78° 77° 76° 45 Piedmont 65 Southeastern Plains Ecoregions denote areas of general similarity in ecosystems and in D 45a Southern Inner Piedmont 0 65c Sand Hills the type, quality, and quantity of environmental resources. They D 45b Southern Outer Piedmont 0 651 Atlantic Southern Loam Plains are designed to serve as a spatial framework for the research, Level III ecoregion assessment, management, and monitoring of ecosystems and D 45c Carolina Slate Belt D 65m Rolling Coastal Plain Level IV ecoregion ecosystem components. The approach used to compile this map is D 45e Northern Inner Piedmont D 65p Southeastern Floodplains and Low Terraces County boundary based on the premise that ecological regions can be identified 0 45f Northern Outer Piedmont 66 Blue Ridge ----- State boundary through the analysis of the patterns of biotic and abiotic 0 45g Triassic Basins 0 66c New River Plateau phenomena that reflect differences in ecosystem quality and 0 45i Kings Mountain integrity. These phenomena include geology, physiography, D 66d Southern Crystalline Ridges and Mountains vegetation, climate, soils, land use, wildlife, and hydrology. The 63 Middle Atlantic Coastal Plain D 66e Southern Sedimentary Ridges relative importance of each characteristic varies from one D 63b Chesapeake-Pamlico Lowlands and Tidal Marshes D 66g Southern Metasedimentary Mountains ecological region to another regardless of the hierarchical level. 63c Nonriverine Swamps and Peatlands ® 66i High Mountains 15 o s o o 60 m; The Ecoregions of North Carolina map was compiled at a scale of D 63d Virginian Barrier Islands and Coastal Marshes D 66j Broad Basins 1:250,000. Compilation of this map is part of a collaborative 30 20 10 0 60 zo km project primarily between the US EPA, USDA-NRCS, NC DENR, D 63e Mid-Atlantic Flatwoods D 66k Amphibolite Mountains Albeas well as with other state and federal agencies. Comments and 63g Carolinian Barrier Islands and Coastal Marshes D 661 Eastern Blue Ridge Foothills ? Equal Area Projefion suggestions regarding this map should be addressed to Glenn D 63h Carolina Flatwoods D 66m Sauratown Mountains Griffith, USDA-NRCS, 200 SW 35th Street, Corvallis, OR 97333, D 63n Mid-Atlantic Floodplains and Low Terraces (541) 754-4465, email: griffith.glenn@epa.gov, or to James Omernik, U.S. EPA - NHEERL, 200 SW 35th Street, Corvallis, OR97333, (541)754-4458, email: omernik.james@epa.gov. APPENDIX B. APPROVED JURISDICTIONAL WETLAND PLAT U.S. ARMY CORPS OF ENGINEERS WILMINGTON DISTRICT Action Id. 2007 3148 067 County: Onslow U.S.G.S. Quad: Jacksonville North NOTIFICATION OF JURISDICTIONAL DETERMINATION Property Owner: Weyerhaeuser Real Estate Development Co. Agent: Land Management Group Inc. Address: attn: Sandy McLendon attn: Wes Frvar 1412 Eatonton Hwy Suite 700 P.O. Bog 2522 Madison, GA 30650 Wilmington, NC 28402 Property description: Size (acres) 2500 Nearest Town Jacksonville Nearest Waterway Bachelors Delight Swamp River Basin White Oak USGS HUC 03030001 Coordinates N 34.8542 W 77.4581 Location description The site is located iust north of the intersection of Rhodestown Road and Gum Branch Road on the east side of Gum Branch Road north of Jacksonville Onslow County. Indicate Which of the Following Apply: A. Preliminary Determination Based on preliminary information, there may be wetlands on the above described property. We strongly suggest you have this property inspected to determine the extent of Department of the Army (DA) jurisdiction. To be considered final, a jurisdictional determination must be verified by the Corps. This preliminary determination is not an appealable action under the Regulatory Program Administrative Appeal Process (Reference 33 CFR Part 331). B. Approved Determination There are Navigable Waters of the United States within the above described property subject to the permit requirements of Section 10 of the Rivers and Harbors Act and Section 404 of the Clean Water Act. Unless there is a change in the law or our published regulations, this determination may be relied upon for a period not to exceed five years from the date of this notification. X There are wetlands on the above described property subject to the permit requirements of Section 404 of the Clean Water Act (CWA)(33 USC § 1344). Unless there is a change in the law or our published regulations, this determination may be relied upon for a period not to exceed five years from the date of this notification. We strongly suggest you have the wetlands on your property delineated. Due to the size of your property and/or our present workload, the Corps may not be able to accomplish this wetland delineation in a timely manner. For a more timely delineation, you may wish to obtain a consultant. To be considered final, any delineation must be verified by the Corps. _ The wetland on your property have been delineated and the delineation has been verified by the Corps. We strongly suggest you have this delineation surveyed. Upon completion, this survey should be reviewed and verified by the Corps. Once verified, this survey will provide an accurate depiction of all areas subject to CWA jurisdiction on your property which, provided there is no change in the law or our published regulations, may be relied upon for a period not to exceed five years. X The wetlands have been delineated and surveyed and are accurately depicted on the plat signed by the Corps -Regulatory Official identified below on 10/8/2007. Unless there is a change in the law -Pr our published regulations, this determination may be relied upon for a period not to exceed five years from the date of this notification. _ There are no waters of the U.S., to include wetlands, present on the above described property which are subject to the permit requirements of Section 404 of the Clean Water Act (33 USC 1344). Unless there is a change in the law or our published regulations, this determination may be relied upon for a period not to exceed five years from the date of this notification. The property is located in one of the 20 Coastal Counties subject to regulation under the Coastal Area Management Act (CAMA). You should contact the Division of Coastal Management in. Washington, NC, at (252) 946-6481 to determine their requirements. Placement of dredged or fill material within waters of the US and/or wetlands without a Department of the Army permit may constitute a violation of Section 301 of the Clean Water Act (33 USC § 1311). If you have any questions regarding this determination and/or the Corps regulatory program, please contact Brad Shaver at 910-251-4611. C. Basis For Determination The subiect area exhibits wetland criteria as described in the 1987 Corps Delineation Manual and is adiacent to several tributaries, primarily Bachelors Delight Swamp _a tributary of the New River, a navigable water of the US D. Remarks The site was visited durine two separate site visits on 11/28/2006 and 12/5/2006 The site was also h d? rologically monitored by Land Management Group Inc. ** All Maps are being returned to the consultant for distribution. E. Appeals Information (This information applies only to approved jurisdictional determinations as indicated in B. above) This correspondence constitutes an approved jurisdictional determination for the above described site. If you object to this determination, you may request an administrative appeal under Corps regulations at 33 CFR part 331. Enclosed you will find a Notification of Appeal Process (NAP) fact sheet and request for appeal (RFA) form. If you request to appeal this determination you must submit a completed RFA form to the South Atlantic Division, Division Office at the Following address: Mr. Michael F. Bell, Administrative Appeal Review Officer CESAD-ET-CO-R U.S. Army Corps of Engineers, South Atlantic Division 60 Forsyth Street, Room 9M15 Atlanta, Georgia 30303-8801 In order for an RFA to be accepted by the Corps, the Corps must determine that it is complete, that it meets the criteria for appeal under 33 CFR part 331.5, and that it has been received by the Division Office within 60 days of the date of the NAP. Should you decide to submit an RFA form, it must be received at the above address by 11/8/2007. **It is not necessary to submit an RFA form to the Division Office if you do not object to the determination in this correspondence. Corps Regulatory Official: __tj flue?' Date 10/8/2007 Expiration Date 10/8/2012 The Wilmington District is committed to providing the highest level of support to the public. To help us ensure we continue to do so, please complete the attached customer Satisfaction Survey or visit http://www.saw.usace.army.mil/WETLANDS/index html to complete the survey online. Copy furnished: McKim & Creed 243 North Front Street Wilmington, NC 28401 NOTIFICATION OF AI)MTNISTRATINT, AI' TAL 01'TIONS ANI) PROC-TSS ANI) RU'QUFST 110R APP[ A , Applicant: Weyerhaeuser Real Estate File Number: 2007 3148 067 Date: 10/8/2007 Attached is: D See Section below INITIAL PROFFERED PERMIT (Standard Permit or Letter of A ermission PROFFERED PERMIT Standard Permit or Letter of ermission) B PERMIT DENIAL C APPROVED JURISDICTIONAL DETERMINATION D PRELIMINARY JURISDICTIONAL DETERMINATION E SIV IION i - l'lik I01bMin,, idzriLili?; your ri,ht? a-nd opiitons rC1-'ard1n2 a<<<?clr>>inistrrlti?c ap[)Cal 01' the abo%c dccisioil. AdLilt oral H]rormLt',1on may hC l0Lilld at htiiV or ( orps r?:,alauons ??t ; (Tk) fart ; 1. A: INITIAL PROFFERED PERMIT: You may accept or object to the permit. • ACCEPT: If you received a Standard Permit, you may sign the permit document and return it to the district engineer for final authorization. If you received a Letter of Permission (LOP), you may accept the LOP and your work is authorized. Your signature on the Standard Permit or acceptance of the LOP means that you accept the permit in its entirety, and waive all rights to appeal the permit, including its terms and conditions, and approved jurisdictional determinations associated with the permit, • OBJECT: If you object to the permit (Standard or LOP) because of certain terms and conditions therein, you may request that the permit be modified accordingly. You must complete Section II of this form and return the form to the district engineer. Your objections must be received by the district engineer within 60 days of the date of this notice, or you will forfeit your right to appeal the permit in the future. Upon receipt of your letter, the district engineer will evaluate your objections and may: (a) modify the permit to address all of your concerns, (b) modify the permit to address some of your objections, or (c) not modify the permit having determined that the permit should be issued as previously written. After evaluating your objections, the district engineer will send you a proffered permit for your reconsideration, as indicated in Section B below. B: PROFFERED PERMIT: You may accept or appeal the permit • ACCEPT: If you received a Standard Permit, you may sign the permit document and return it to the district engineer for final authorization. If you received a Letter of Permission (LOP), you may accept the LOP and your work is authorized. Your signature on the Standard Permit or acceptance of the LOP means that you accept the permit in its entirety, and waive all rights to appeal the permit, including its terms and conditions, and approved jurisdictional determinations associated with the permit. • APPEAL: If you choose to decline the proffered permit (Standard or LOP) because of certain terms and conditions therein, you may appeal the declined permit under the Corps of Engineers Administrative Appeal Process by completing Section II of this form and sending the form to the division engineer. This form must be received by the division engineer within 60 days of the date of this notice. C: PERMIT DENIAL: You may appeal the denial of a permit under the Corps of Engineers Administrative Appeal Process by completing Section II of this form and sending the form to the division engineer. This form must be received by the division engineer within 60 days of the date of this notice. PROVED JURISDICTIONAL DETERMINATION: You may accept or appeal the approved JD or provide new information. • ACCEPT: You do not need to notify the Corps to accept an approved JD. Failure to notify the Corps within 60 days of the date of this notice, means that you accept the approved JD in its entirety, and waive all rights to appeal the approved JD. • APPEAL: If you disagree with the approved JD you may appeal the approved JD under the Corps of , Engineers Administrative Appeal Process by completing Section II of this form and sending the form to the division engineer. This form must be received by the division engineer within 60 days of the date of this notice. E: PRELIMINARY JURISDICTIONAL DETERMINATION: You do not need to respond to the Corps regarding the preliminary JD. The Preliminary JD is not appealable. If you wish, you may request an approved JD (which may be appealed), by contacting the Corps district for further instruction. Also you may provide new information for funther consideration by the Corps to reevaluate the JD. SI:C' 110x' 11 - 1:I:O111-'ST 1 t)I: A1)1,1-r11_ or 0101"('1 1ON? I I\lTl11, 1)1:01,1,1 1, 1) P1:1)\IFI REASONS FOR APPEAL OR OBJECTIONS: (Describe your reasons for appealing the decision or your objections to an initial proffered permit in clear concise statements. You may attach additional information to this form to clarify where your reasons or objections are addressed in the administrative record.) ADDITIONAL INFORMATION: The appeal is limited to a review of the administrative record, the Corps memorandum for the record of the appeal conference or meeting, and any supplemental information that the review officer has determined is needed to clarify the administrative record. Neither the appellant nor the Corps may add new information or analyses to the record. However, you may provide additional information to clarify the location of information that is already in the administrative record. 1101\ I OF CON 11('1 I OR Q11FS i IONS Oh I\I'O1Z\lA ION: If you have questions regarding.this decision If you only have questions regarding the appeal process you and/or the appeal process you may contact: may also contact: Brad. Shaver Mr. Michael F. Bell, Administrative Appeal Review Officer Project Manager CESAD-ET-CO-R P.O. Box 1890 U.S. Army Corps of Engineers, South Atlantic Division Wilmington, NC 28402-1890 60 Forsyth Street, Room 9M15 Atlanta, Georgia 30303-8801 RIGHT OF ENTRY: Your signature below grants the right of entry to Corps of Engineers personnel, and any government consultants, to conduct investigations of the project site during the course of the appeal process. You will be provided a 15 day notice of any site investigation, and will have the opportunity to participate in all site investigations. Dater Telephone number: Signature of appellant or agent. DIVISION ENGINEER: Commander U.S. Army Engineer Division, South Atlantic 60 Forsyth Street, Room 9M15 Atlanta, Georgia 30303-3490 I Dal US Army Corers of Engine-ens Date: October 8, 2007 ATTENTION PROPERTY OWNER New Guidance on Jurisdictional Determinations On June 5, 2007, the U.S. Army Corps of Engineers (COE) implemented a new method for performing jurisdictional determinations (JD) pursuant to the Clean Water Act (CWA). This new process is a result of the recent Supreme Court decisions (United States v. Rapanos and United States v. Carabell) and now requires the COE to conduct extensive reviews when determining if certain waterbodies, including wetlands have a significant nexus (connection) to Traditional Navigable Waters. Since this Office has reviewed and verbally approved a jurisdictional determination for your property prior to June 5, 2007, we have finalized this JD using the previous process. However, if you, as the property owner, are interested in having your property evaluated under the new guidance or have any questions regarding this matter, please contact Brad Shaverat 910-251-4611. S. Kenneth Jolly Chief, Regulatory Division MAP - NOT TO SCALE SHEET 14 OF 14 SHEET A3 OF 14 N W E S N.0 GRID NAD 83 SHEET 10 OF 14 SHE T 110F/ 4 i Y SHEET 12 14 SHEET 9 OF 14 i' i SFIET 8 OF?14 ]WSEf TB TNAr WS -01` 7X15%T xes A.w r-NUms Au ASEAs a wAices:vn"AWS I-LA rzur SLANT IL SECS CIEw WiW AcrAS tt RYA CNAMi M W IAwW OARP'/BL9A0 NEYILARa5 iroi ro nicNrc RS s MOAT, "rNs L. a RS' " xc?`"ANOBLmG nu" ATO`mh WA Ps US AMIY C/p1fPS fi EN?f1iNCFAS REMRSENMIRE _ IN fFI' I`MX;v RE _ 1918hta} IME FOR LOCAIMC XFn OCAT WITH S ONO "I I MS Ell -ANTLNNA M'.P WAS SE s PR0.S LYNY R[ MAMUL 1-0 crcdxMMWroE?,A _WenyPON rmenr cuawA cEarNCRffWY-Y (_l) DiE NL95 BA,Z 5uW NEw Bpa MG (UF. 39-ID-19.92 WB M L? ?M.ULHK AbI TSWC ANOAMAT EASrID xs LYtiAM1MlAL Pb._ MW )RE?p, AT 1 SECLW9 SM'[)6PGVCU$ RfApN'C9, MW BBASE STASACMAL-55CY![W RIEWEE7RENIIATLY N01FS 1. ALL WSY Cf9 ASIF HMHAViAL WANG AY US 414mV fFET N%h'S OIHERW SWAN COYBPED FACTW G.9998', 2 SEABNNS BASED UY NC WO (WO W) C S Bb. S NEAEPANl - BOON 2N0 PAX 916 A SWLEiAP MAS MN W M4ESRGADLW LIP -NT SEAPCN A'OP EASEMENTS Q RMWa ENCIMBR.= REST 0"w LGkNmm OMAERWP, BRE ENOpKE Qi ANY OR FAPR TMAF AN AOWRAR AM bLWPEN VS VW? V VS ME .S WN awY MIEPt' ABOIfW b. SLH. A? AND [XMPLMILYTAL CLMY1NY15 MNL NVr EYAW&D ER C? AS A PART C ThS SLWK.. NO SrA1EM9lr IS A ? R Ek5RNCF a t9S&ICA%AIO W OKPV O rANM3 OP EApMTWS "AT MAY A-T - USE OB orAxawWAT OF mrs MACr >. XEUTANAS'_AN. ON WT-ttU ANON BYLAW AuNAOEMENT (xWA= d SJ&ACT N ALL FASENNTS -1 OF NMM AAD W LNCUWPMT£9 mnT MAY a 7777 nas-1, Il RN NC CNhW'ATLY fNCYN d imS PLAY u(RF W 51f0 BY (V(K CFS C&S51.1 4 USN' T -5LIF S1W R[[YIIERS THE RAW PAM IIAB SENT !0 INE NANQN& C-WSIR 5URY£Y- PNW£SSAYG I6 SNE£TS P-9 ARE- ..'S pVLK LEGM * NN Mw AWL WWAND8 TOTAL ARRA A-,,- 59 R NIA rB A- N'ATIM OF TM l6 TOTAL ANEA 19,-. FE 0,. ACRES SCALE I" - 1000'- 1000' a 1e? aoo Eaao ,aW SHEET 7 OF 14 A FICM&aZMD 243 IAIYINCTON, NORTH GAOIINA 16401 TILE: 9110) NYIWB FAX 910)151-8267 MIR://rmmdtlmvatl.bwn 0 wo 0, w cr WETLANDS DELINEATION SURVEY PROJECT M ` 009100163 EARTO C FOR PROJ,SVYR ; 0lJ WEYERHAEUSER REAL ESTATE ORA m By :Acs SEAL LAWS P DEVELOPMENT COMPANY FIELD BK.: W1013/56 - LJ coup. FILL: wnDl-aosla91s31t .=` PORTION OF ONSLOW 19 TRACT S EET H : SHEET 1 OF 14 ate IryJ[ Fl?,r MCIAAAWS 20WNSRP - ONBLOW - NORTX CAROLINA 1..99.0 June Z0, 2007 SCALE: I" - 1000' DWG. N M g5 m g < m v LIE c WETLAND. RAG TABLE MC NQ BEARING LENGTH NORTHING EASING G C4 34 3.4 4 .4 144s1an x.u6Bn c7 w ' 46]111 39eux1 1.x.4 s ClA NIZ14'171 1267 31.25 M 12m -4 2 246965155 119 MM13'51'E 0,1(1 %64 115)1 316666{b) 119 016 59 5411117 2164PA.01 214744.1 C10A 266472.1 3989!,1 CI 45.110 8466180,95 CA cu 4x LM 721111164 411117272- 2.sn. n> 4V wesx4 72649b1 2aee4ul 94861.92 017 CI6 7940114 31627272 14644172 346960.192 C ]e' 45661. 24 1116 Gig N-E .7' M.45 W JB.xm 31.7.7 7466/1881 61 34411.4 G 3%31.64 2V Cy+ CS2 'A6D0.. 34611241 73,11 2 2.64442 G1S 111 f 72441.16 39411.7 114DIa19 3V68011Po 111 C27 30194.4 4194.3 240117201 24904.3 CR 744211 24812229 G1 111 N?44-E W,21' 9401811 N317.ll 4-14724 1411564 030 41.5.4 2481..10 G+ ry ",ad 4315.15 721141.3 2491111 1-4772.1 CU P5 4729.7 14914-05 m 4]216 . 391211. 1 .B7 248=1.19 114 3411131 244723.- 72321-01 2461100 cm cu 72313 :14244 072 Cw 3134.16 3414)4 7464 n 214711.7 401 Lw 4]14.1 54307.91 xle6va4 214369.14 04 w154.te A1441611 CVM 11. 475w.91 2-11(1 w]A 114 -21WIVE 13,w 31746.36 39711465 214.619 24449.67 131 597IJ6.97 2.65410 CAA 34' 59730.10 344672.4 M2A GS 7. 3464 MIMI. x16451111is 1444659 =A CMA N=1'0?11` 1 r N10 5740.. 58745.6 ae4s3 1.14.m CY 1.N' 39741.94 2441.00 M7 C51 3.17 816' 7211164 JBDY14 7441. 21641'7.3 1159 ]B' 4 4116911.7 1111461.68 111 qt 4' 546467. 844.1+ 2-707.4 0111 381111.1 1 b1.' 7111.30 -51 2-]51.71 W? 4Z]2 51244 21641013 1195 016 4.]4' .4' 39616.3 596314 249701.511 1.972].72 37 CW n' 45414 514464 2.91144 1444233 15 s9xmu x14172 L70 4414.4 2466/10.14 044 .4' 72552)14 21641.4 Olz m 19464.111 244651 073 C7 . ' 5941x53 %41510 2411472.47 34411699 075 5 Y 5171151 245141.4 676 C77 421-111'WW M26 794461 -113672 -11- 146411 c3 -47 244851.71 30 4846.M 06 24111.{ 114 7241)720 21 12 33 x I movwtiriv As 544)_11 3.41. 15 m.. 141464 2.81964 Cx WS - 3414.3 4 24432.55 2 7211 -111. 7241601 2601721.15 CB1 1 2 721.96 114 114 Mi_. NI May ?70' .0-. 14.26 342401 2 7214 249 111 rn r 71x16.. 7 2.9755110 :MnSSs 119E 41210.4 301144 - C1 Cw rw W 411.4 4971 0,7. 2.191.17 2mu.>7 1195 Npmrf4if 2&4X 1"...42 249750.1 1101 4940.65 1 17 %9466.. 249)611 611 u 19 Cif 7 TAT 716651.. w-v 24874.37 CI01 4 n 3 T 60 CiOE 4 316517.4 x461621 mW 41491 24936172 clw 372584 491992 74614.51 -14 444 Sim Con 1 544111 1.940.1 CIS 5 61451.4 4863. 7111911172. 314@724 01119 CIIO 1 44,.4 51583.4 x.-10.94 21456151 111 X % 374.17 24_.1169 0112 46 72114.17 246111.. 44 72 m" 6114 379111 -6994.4 CIIS 6662W 17' 5441.1 24100164 0116 M-)e' .4441 0118 - saws' n -044.711 111..4 014 0119 N61'1'm p 49.14 4641.16 11118.52 2{3151.19 020 %941198 147017092 121 464 13C40.a <IA 1 199{ 47 211011. .23 CI1 N ' I N - T MM.A 69 24318.4 4 11 11118 1 V7 11110.3 1• I 781610.4 1 .4 127 Ow ME) 746264 3002.47 2170110.32 241. LIE T5W WETLANDS AS TABLE FLAG NO. BEAAING LENGTH NORTHING EASING 7500 3L411r.T 11 ]7 40LWLm 216472663 1501 9 '99Dp;L.. a' ,441] 2454551 1502 143 5511 40460.4 4142112 246110.4 21414.4 144 115 )1 .144 642150 10413.01 24.21. TSY 4514 147)8.06 IWM 44.4 ]50] 7701 SJV' 1011 .34 +.]10.17 14 .4 141113464 49' 1 4161,11 . 215455AV r1o 1710 441191 1:64].1 LIE DNA WETLANDS FLAG TABLE FLAG NO. BEARING ' LENGTH NORTHING EASIING P0. 140734 3-01150.05 1N4 1172 444691 249241.17 O I '4' ' 4607201 2169111.21 Nmm 101091.4 x.172.81,. LINE AN WETLANDS FLAG TABLE FLAG NO. BEARING LENGTH NORTHING EASTWG 4Y 49010.4 101013.21 2 .. 2476660 JM] AW { ..JR 4601101 406019.01 2.767.67 2.74..1 016 N16 MLVIL? 2&5,r 46065.56 444566 24]14.1 21475441 AM7 - 4410).3 311111171.12 .1 N 401115262 24370.50 AM. ANIO 11.41WE 1,13?13M M.51, 27.77 40111-.62 41177.4 246710.62 216362.0 AM11 1 a m032 3.311.52 .12 1 N1 JS SY aM11bi 2.311.. AM13 AMi1 T 1 40621QBB 40611221 2435).66 243711 AM" 412761 2.1064 AMI6 1111 w612.W 1424.3) 24]11.4 -- -is N M7.0 247"6651 AM19 A m N-16'. I M74' 1431.13 11111-0.72 24 III4L51 x.764 . M 021 N 4W3s51 . 241551.1 AM21A AM. -114A 40538162 2.7114. 24357.1E - AMZI .2. _X2113=12- 4647.7 4081NIX 2476/161/ 24116]2 AY15 a11A,9T 24195684 AlI1] 6643,15 2 .1 AM1 AMA .?ISTE -17' I4m2W 46541)5 21501., 2484n.1 AMID V04A.13 24613. AM51 66641.1 241310 AMJ2 14.9.60 24453.76 AMY N 44)5572 ,44.11 9.4X.11 24 1114 A11 10540.10 247247 AMY 40184,61 2472.52 .0111 40714.15 436194 24723.37 24M75.71 Awl AMU .74242 w710904 2441. 2441.5 AMk 1.r. Y 01.1 671720 2 14mIQ11 2. m AM47 J w 1 2. .14 M4 AM+A 471924 w.1x 2.7MI0 2461-6.4 AM1A ,vww a .3 444..11 1+1176.. 2. man Y4 72142 N 2 42: 1 ,37172.111 41".56 1144 91 Awl 407241 P. JI AMx '4 ,11251 24411E. AM4 AM56 .man 01231.% 2467114 146723.02 AVm AM4 wols" =7V 4072454 671724 2.1016.4 24 17216 1 AM4 4 W1P411 64.1 A- ). 6 2151%7.05 .. AM4 W 1. 0 2 434 ' . .01 AY63 AMq 'l 0 4MM. 24711194 2 AM4 N721CWE 47."' 0 Au4 1 4 AY61 x 0 15379,G.64 :roman AMA 071 17 41 2.775158 AMn 11,1 0115 AM]a 1 E 1w rE 11.1 4 on& 41115x61 2444 36 ;.IMC AM3. 39 3 I' 63124 2475-11 .1. AMn P 7' 07653,52 6114.25 16 51 .62 .7a N 677.15 103103 72472 x 4132.67 34317 AM4 AA4 40md.a 471961 74)114. 243x02 Awl 4 14 4151688 2476631 AM, N 41- 634.1 2437216 AM. 410.5 Hir4'Vl7*E 4' 1033,4 472123 1415114 114621.. N7 6A1.1V 2!634.4 NO SCALE LIE NA WETLANDS FLAG TABLE FLAG NO. BEARING LENGTH NOR NO EESRNG NAI 1010,tl .1672 .4 2414171 V069165] 119)47.0] NR4 +0414 2424A4 NM -WC 21,M- 1493. 67282. 21414.4 24614265 .AI -11- 646..4 2474.,4 x4411 40°72..3 4tl651.6 7+166x11] 7.75172 xA+O x Y:. ILYOW m 27 w21 N41' . S +o?en1 m, x4 7407 NAIf UTH'P 4048661 24767606 NA4 ?MTVW'E 2713' i --NAI5 480121 2.7604.06 NAI5 NAIB 1060154 3.31.4 3472 NAT] NimilaWE .16 27263624 E470A1 XA1B 41143.. 411672 24070a.61 NA= 4411721 2.174N NAZI_ 10612641 P.n4A _ NAP] 10460.4 167776.66 E-3 106161.r 24141.17 x1 5 114.72 2.7601726 .3 NA1 4061124 4611.1 44741-01 14638215 NAV 141:61 xu1461s NA1 S7419'OrE 17,17' 442414 2 NAA 406211.- 2 Y RAID 106216.91 2.790115 NAA 10621661 NA. NII21.12 211111.72 NAM 724211.4 01m6.88 werlu 24.0121 248601666 741144 61 NAl6 xAk 4Br1.W . 246 .1 N.437 40846485 Pkm44 448 1 10111.4 2.6011.61 w2eau 7+1143.1 NAw 10626662 E 35 H- 'W ry I1,x 1W?]6W 1411245 2 v6 x.131- A W"'52"if 11- 106271.02 -1.- ,A. NA. 1 101151 481550 3.772395 pA47 106114.11 11 A, N f 101314 .61564 1472113 E1e724- N 461x62 2.1. _ HA60 A51 4641.4 1141.08 24741. 21 2.aT..6o NA53 10x3727 2.451.73 44724 x . now 146-4.. I z.49au nA4 ITT ' 1 491514 2 11. 4 NA nu] 4' 401.1 444x1 -1.M z465T65,- ml m 1111 NASA 145114 2.mY.. NAa NVI 406 466 2.616165 xM I - 2 1 1 N41 mw 7 1014724 4 .8150., 2.8&71 -ABA _15L78 3.4251 NMb w430. 2.401. x721 4676.W 01 441.50 x47 483017 24401.61 NAU 44744 :411111x, N4B 10676x4 3/400.561 NA70 run HIMWE jail 106631.4 111 1 3 2.80667 NAn N107r3rw -- - l'.. .14 2168017.4 14 5 N _4. 411 64. 2.416. 71 .15 2.41161 M NA 3 44x3 2.61565 Ii N.43 NM- N .01 2 RAr] 6141 344I433.46 1478 1 105 2.444.43 x7272 x.o n 474724 {14].41 1+4444 741144.4 NA4 40.25 4 11 2 .401 NA4 x7264 11621 ,7 10111}1' 2.81 17.18 2.814.15 x4s 19.6172 : Ia1 x724 472461 114141 NMI .Aft I 3 10]104.. 411131 b6 14120.51! x724 r 4.1.46 sw44a 61411 2 .q NAK x72/2 '4 an N.91 21471141 NAw hiollml, I— 4071N.111 a.BA i 211163111 NA4 N-WE 6.172 147764 NA" N 1 4.4.71 wn7a4 E.461.- x+114661 . IN 8 ME N4r42'N"E 3-W 10.6727 2.6,84 4NFIQM&cR= 243 NCAW FAWH STREET WILMINGTON, NORTH CAROLINA 26401 1LL 910 743-IOw FAN 810 251-8482 http: //•An.I4M5a11xAmm ATION SURVEY WETLANDS DELINE Iqb 0 46,E tq R ffu WEYERHAEUSER REAL ESTATE as 6 DEVELOPMENT COMPANY PORTION OF ONSLOW 19 TRACT L FICZJL4MS MYNSMP - OM4LON - NORM C'AROLW'A ..5 ,n June 29, 2007 NO Srux PROJECT I: 009100163 PAOJ. SMYR: DLJ DRAM BY ACS FIELD BK. : W1013/56 - LJ COMP. FILE : vLo1-009100167 F SHEET I : SHEET 2 OF 14 DING. I: LM ON WETLANDS L!E ON WETLANDS (WLAIMI®) LINE r WETLANDS FLAG TABLE FLAG No, BEARING LENGTH NORTHING EAGTING E. -_- 407011147 .9w6.5 4711., 7441.65 F6 f 'W 4691' 10684.11 164437 ro N 'W 4446.01 464489 E4 1 404172'17 21641. 6 9 .1. w70..N 24531.1 FI ]I'W 1 ] 6724,19 24472A4? ?re ?? o m v LIE A WEMNDS FLAG TABLE FLAG NO. BEARING IFNGTH NORTHING EA511NG 412 21408.91 9444x." AIt M10 NG577'%'E 2&w' I IE, 41470.10 246305.4 2017166 4,09 wham 04141071.18 A5x 465-SVial, .11, 4044.0 2.-a.m AM7 Ata NM4!24E 52.W 90184fi18 .41NUl 4.1107.19 1M4IM37 AX3 ANN N -1420 41415841 44416121 Na=m AX] ?6.X 214425.50 A301 -.50,66 144421.17 A301 414107,07 b 2 2 440313. Am AM S1t.2z:5I .1- 104434,89 2843x0 4,27 __ 4018]1,11 241443176 AN5 Amy 40031.12 4025,13 2414459,76 24448182 Ala 4,29.3 405081.12 105x2N 26166 .m A291 115_7 l.M. 8015".X 4,291 4150122'1 510.0 A Am m9 40517.4 405117.43 24151259 4,206 NgXjjI MM 24451.3 Amt wl _w SWI N 244160.10 Am6 A - 4161162 /S1k0 2KKin? 21&111.22 N" m A 111 -Hi4" wsiw.xi 185 i Ami 1510.38 ANI Azm 111'x2 41615811 105107.33 Ann [ ff Mm lt6 T 46506Am A n A2ia I-4,0613 ,Ii -.BB W Any A2 iC 4119406 401x1.66 244&261 20454,35 A273 A272 4 I 41484,10 040815 34541510 414485821 Alm Ala 4! 7 406215.41 424].10 245490111 2449412 Ala 37,47 405115.10 Ala A265 N51-O'21M 37.21' 105,514 105165.]3 4464x4.5 2041106,44 A"! .57WW'E 46.36' 05206,75 105210.05 204118 A192 7 W52211 2.X1166 A"I 4,160 XI NS t4, 31 4144411 24550554 20664,4 A16 i ' 46529202 9 M 6 A57 A2=0 T. 5al 41526660 055080 31x20 246111.0 A2X 506 1 .519532 . 4. 52 Asxi MITI n,", 4044210 0911.01 A254 A253 .64=31 X 1' I' 110101. 4X150,15 2MN1a- 1 45.14 5 E 4 I -nal 1155344." A1X 1 24653511,83 Al. 405249.19 2465314.83 APM A21 S0- 43.- 4502.41 1'9 .x 140019 24 SNITWE 47.9v 121.81 0647.66 A2w AIM 405014.11 49794,1 14009.50 2465116.19 Al. Y 4100}ID 2MatlV1 A24P 041092 945114,10 4,21 1 14464,44 =4651x.06 920A 2 0054,63 11500183 A2 ATM Y ] 4047MIS -4438.11 2"641.66 am 7 n4Y wM am 41414260 2465411.61 4404444,2 04010.85 2044238 A1. S? WE -11 01611.11 20 .M 'M'F 4081836 24X2 5.11 1 1o'1fi2 245X5226 j 1'112 2.45x60 9 .'2'E 41.66,. 4a6E-1 21.69x0 2444511 e NIS. Ia3614 3.0684- 2.X".74 I 1 Y 1' 1• IaNL" 245140 A"3 N.1.1 aI 447654 2165764.V2 AM 'W 3 04444,54 26x1 M A2xl M IMXM 74x" X An0 4,19 9 101364.18 009691 205110.41 20572373 A=le -.tAX 2"W"M A 1 - 0.6121 405x.10 246X..5 3 4.44 A215 X M 4a37 M 2M5mle 4,24 3 'w I'll 1.84.15 4a15653P 216x674 -55501,11 A212 41 41402800 34641,0 A211 44 2' 4x4¢12 2IW614 0 AIM -IIII -IT IS— 14730.39 2454-4 2 95 19' 1 A2W M, 4a"e.m 2011t1AE Am6 3739' -MM.n 2 I Am3 Aml NI AY I III Ix1E5,9 2.5467 A2M AIN N 01"55 401"&4 18 2400.32 ADM M T 4150X," 2 Cl 246440,63 .. X 161 61 240 11 IN A19a .1.1 muzu'w 25.0V lSI 41510731 1011 1.01 B6 24x1607 N . 4,14 2097 2050856 Ala N • 1044072 245541293 Ata 44,1 0851115 2.5309.10 AI AiM I 566 1xi.." 2.550 . 444 A191 AI N .1 15410.91 1443266 - M. Al. 195411.66 2145817, Ale ea] 3 N AIN yn."VE 405381.16 2.55916 AI 10667609 14841284 AI Al. 107131 4163"4,9 9 P 6 Albs 0 21 Af7 AI- Ak92' 4 N 1527719 ¢ 66 2M57M.W AI" AI7B 1 4142, 116 4 2.614.- 2466750." All 866 265]4,07 A174 SII I.., 45414 M P B A175 Q0'42'lI'W 26,41' U 474 24667xM A+- W110"71 II 114887 7 .2 A172 Ain 0 gal -72.72 24x191.38 Am 1X10." 2-3.0 IS w 265841418 A%7 141610 .OS 2464.11 2450".9 07x05 24493281 4,166 754 1 i 4511607 04'41 2466X3.10 0.696- 1.3 1]0' ' IOM'" -X061.82 u I - 4x13215 006"651 4,17 A14 S, I" 1X"4,01 4X01608 2.144.. 1 A1X A=t IS ", INTI.16 0.91,4 2M6"551 21&038,50 0787 00X50 AIx _71.67_ 11881.2 m All. All. 4TT1V3rE 112' 4X14," 24617.10 24&121.1 475] AIN Sm4v4Q-I, 17- 46x662 10XM.W 244611382 2401". .11 AIN .X74,1 0.4,02 2. .k 244257.0 AIII 1124,50 Y ]4,-30 AI. MJ'WISFE 41.39' 1449166 2M All Al. 404421133 A1/S ?l 10V " 703. Alll 147] AAA 101 XN =2. -,SS 1-66.0 LIE A WETLANDS (CONTINIJED) FLAG TABLE FUG NO. BEARING LENGTH NORTHING EASTING 440 AIX -Orl 27,77- I4 01811.77 21xk2m 24655.61 Rik -4Na 2-14 A137 R i4NM914 AIM ' 40.7,38 24115020] Ilk Al. A -.8701 Ill3A62 11x443.56 246415,1 A'. 4010130 ^. .446 3"51 AlM 4047223 21S 34 A.1 Al. 40-5." IDI647m R1ee5..06 x4.1721 Ain 10x6.50 H065aX Alm N-- 111 ISAV -VB11. --3S VI 415 U8 2406X0.. Aim 14X66 1UeX69S Alm Al 24 +owM.66 94883822 256351,54 A123 Narlwal" .2M' 01934,70 249646.66 Al. AIN 4018x2. 20644631 218844.50 _ Aim A119 S4zzr*1F 0,34' 104fiY.J2 404OW02 240820.0 x415"51 11. 41.67 24016IB S M 101051.30 24855719 IS 3 .8641 AILS AIN --10.64 41107166 34x".07 24."39 A111 -751.11 141&0.10 A112 -.IS _ AIII 100- x476. A110 4G-MW ¢416 4, 4,1" 40800.10 9-BJM.s 1X M07 er 1160.41 2456260.0 2 .1 A12 4223' 21410.63 241044222 A105 -449250 x4601.$ Aia -148221 141014,0 4,103 At02 -421E )2 214T -4.84 40114.06 208910.11 20X5- Alm NN-_ nor 414-0718 240O237 Alm A11 11NI.X 101-4.47 200ill.. 201010.16 A6, 1.MN 2.7051.. A 41.7x10 26103&07 A. 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AX 51 2 49 .1 -.3613 24H747.17 Aw 31.1 • 1460& 245]' AN ASS 32AV -71 -7=4.15 .731.44 240615853 6" AM 4 1 ? 44' -76661 4471517 -- 66.7-1 AN 9- w.7.09 20677.13 MI m..' x 2-6n6N All NWW4n 4 . -. 24800206 472 A51 M"TITE I 404X1.73 441.14 2.X25.61 IMNN,eI 4,50 sw,nn a 44"4650 x.841111 A. 1 1.04- 0,187227 66466x6. 708B..n 477 101111.14 2 6610 A. 1 26171.& A. II2ClfFQrW 1 411flAx 1.91. 2011X,81 A- xIV "4.- 66+0x610 A- 471 1' -0180 41441,50 DIBxOBOB x166"]." Aw 4aA6a26 2.8.8.73 AM 4510.10 2.54"9 A37 A37 147 41X644 -38013+ 24590664 2455094.61 AM 4,. 35 1' 40512747 1051'61 4466x0,]6 2466X66 A% SSW 41514410 1046616 AM '115017' 105.x.33 2.}0306 4,2 2-380 41312808 $415" 131 4044.02 249083.7 4,w NSI 12117.70 10513566 241074132 241114E6 Al. ' ' ISIMx 41.101+4,1 2607416 2.'616 All 1yq p_ ?jtW bNS.. -I-,SA All _ 4,1/ N091=10'E S, wW6a w6n19fi 24111,.66 241207.10 Ail- 4441x41 xb17ea1 623 4"071.¢ 2 12 All MO • 1' 31.01 661 "127 " 3.71014,5 A18 17 .1' i A- 3 7666 Ate All Nal-MWE 'v 405096100 ID6a-.10 207M7.71 241510" At6 Ais M 1f5g7." 11x.9 254 43166 A1] 40X12,63 101&4,4 2.1.1.5 2111x.xi 472 Atl 110152 401925 2447M 66.7-&W 107 0 swI --W 4164.66 40114,66 AS NlJF21F3WE Sam' 1025,5+ 217MIA0 M Al 4111600 21 218}X1.0 Al M IM -21 10'4,1210 2451X7.82 241574,3 A L .4 3NI54.M M - 54_ 1M4 Al Bt Nu-, 466080,82 207566- LIE B WETLANDS FUG TABLE FLAG NO. BEARING LENGTH NORTHING 415069 91 EASIIING 1 Ai 52 . 40611511 24>SS1.I 1112 R 03 04 Imn,.2 5061X84 2.151-7 iM7 4Am BS - as 421 " w5tB116 2.269.83 3-14666 57 SWSTM-S -62x.41 x4rA2SIz a6 as mV3I'2a'E 35M, -51 0 .52MI2 101310.0 2 1361.19 BIO 4510135 246 381.4 0I 29 " !ti 12".21 2.127.47 812 all w41J.- 054751 " 247 .is 14] 135 615 014 B15 ONXX 2411 241238.% BIB 166=064 24573230 all 405207.30 24720631 M 161%x 241135] SF9 '4 1 IOSm3M 2107X" am 42920.02 24 M.M 622 aJ 41007210 2Mn01.N 2.1.42 all 42424,21 247041.9) 524 am ISIS 01 Maw 4481016.12 826 -015.66 2 X.40 ax] 826 40.41" 05X03] 1. .101081 24610644 a39 41%1619 3461007.07 630 1o 3187164 531 1x01— .0 2111121.7 a 111010 2411-.21 all N+r4V5rE 2D.63' 4allm2i 2011m21 W. all NOMWE +' I .xi1507 40526050 201135.4 2.7111 T 838 B37 05531 .xi"11 246116M 2071550 Ma 12699.10 2411835] 470 IT— I.IF -7S 2-1181M 6- QMNI 2071.0 B0 012 Ile Axn2N -XI 2011Mx 94407".. 80 544 I 105]6" -11- 2S7Z0- x.7066 . B. I' 10x14.50 . 207311.09 SM 10X%31 945154.06 541 4X07.9 2.134891 B- W5fFlO`E -3a 103S9465 2.139.11 544, BX '4'21 I' 45910.9 4,2 4074210 24101.7 BL 852 INISSISS i. 103061.. 2022332 -I.. 862 50 NNwI2*w 24,01' -4407.17 405904. 241121,33 2.1015 ex 4828 2.-64 63A 1• M ua11o.64 10721.& 545 a 2.1Xa1e 541 BX 1' W m IOan . 3.14666 1 0 aro 1v . 1010x10 46720/ 4461"61 BX 428104, 2171165 547 4292814 21720.22 a Y n 2 ll BW 80 _W.1, '11 SV 00x610 x 10199.93 411 14 650 405 0 20T' 1 666 4217293 247140.0 aJ ax 17.75- 415]4 769 2Mn"6P 2.710.9 A" " 166 X 2 ntab 810 611 -111' ryl 1X07.17 40xiMX 2M7055.2 24101066 511 8513 s IRg104 43060.4 3.14238 244106x66 54/4 4414,10 2.10380 4MI2m 4415.50 015 UI I— 4x11730 2. 10 8 8. " Sam "52'47"W ,I 11 4%5651 4x1 31 IM- 2470X15 0121- 207023- eat _ Nnvgw z 40X1670 24701 06 104, 953 __jLQL_ 40X10.0 248 2 654 086 -x-110 40X"13 24E94314 666 1' MAI' 4152 -1 ax ne ` -. • 4oszMO5 xix 41X4.0 m x.e Bap I?JI,2Tn 11 24 2100 N B9 24, 4516. - 1Mam.e9 Bill 19.17 4181"1Z 2 4.6 M 554 665 27.17 711 4518432 MI . 46 1 2467620 894 t.5' I I.k 146 .. 24x774,51' Na 40NIM .5040,. 2416110.17 .1 "] 1 954 --NI -11.1 IT 14,45' .SON.. 060141 3 1 . 2ft B" ? -11 4144,8,0 246-144 8100 SX 104pBI,10 24606&." 477 if, -1&391 11NX94 SIM 47.6r 149x66 0 5103 9104 x N .6' .X30.4 4X052 9105 9066 .60666 6 1 nT nor .3116,52 1 2 054 0 2? MX i' 3 010 BIN, 1 19 wn! 3 013 2i1M I 'I ,i4•, • 20aALM 4,111 Bns 'Ir4'e 44, " 4 N 2166474.& 216611166 711 MI5 11111 4r 1 , 2464060 248661x06 eua 'OL41S May __ aim 2NMN.5 1'66 N50V "96 1 2.xel.E1 a,. M297" 15,15' 451 x 31x.@8.79 812 Bill V E N'7'W.'E NI 40401.. 4621116 P I 240336,7 4,115 T 4x230.fi1 S 0. 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BEARING LENGTH NORTHING FASTING 1721 rr"'ox N N4-rM4fi'W QM QMS11 404666 1.66 MIS 284aU1 24Meaa6 72 na Tlx Lin 414x08 -.3654 1x066.51 2418440.61 21567666 -x,7 Tw6 4 4105,10 246 1 o] POB TAB Tlw 1]07 R OO' W 1604' 151631 .n -665.0 2MX27a4 2.501 2080730 21690627 P4kl"14, n>,4 4x907.66 0-7314 WETLANDS DELINEATION SURVEY WEYERHAEUSER REAL ESTATE NY DEVELOPMENT COMPA PORTION OF ONSLOW 19 TRACT MCHLAAW TOMMIRIP - ONSLOM -NORTH CAROLWA 17'.01 ,- 1..101.0{ r.a a2., zom NO SCALE' PROJECT p 009100163 PROD Sv : DLJ DRAWN BY : ADS FlELO ON. 211013/56 - W COMP. FILE uw101-009100163 R SHEET B : SHEET 3 OF 14 DING. A: LIE PWTIOB WETLANDS LIE NB WETLANDS ?a a n 5Nm s° m v FLAG TABLE _FLAG NO, BEARING LENGTH NORTHING EASING El MI M itav -.5 2-18641 R © IO .4763.34 2 .N 2463189.1 EA. m PL +01x.? 24 7N,W ALDN's PL 9.ONB 9L 11] 141 4041.22 _ 11- 3 N AL016 R PL M) EN n .r 4.137 -x$2.62 x19161 1460512. 13. E12 M __ +N31A55 x4511 21.5).58 2-11.9 ¢. 6..5. 9 1.111 114 N 11X58214 Ele N621Y2a'N 20.19' 2-37 4 5 15 43 2 DO E20 9 -7?AG 247 1 2W 2tn 31 2,15320,141 463 1 N0512,541" 33,93! 4 265451 2x520.23 E2) « 2-EN86 Eli MCI .raw.. 1 2e32aro Eli Na0wWE 27.24' ET. .411.67 .531.. 263: 312 21071.1 02 N2WWM'E .541 s -41 E- .11113 246MA EN 135 x - W NQAWWE 1..51 41051117 1101219 26]251.15 186 Nf x52%44 246320.21 9 E1 -.1 DIST 7555 ! wsJ2.1s Z 7 4I6JJ12 E3B N + . 21 2 f. E NMM'03T 4711 . f' -2 9 .903V w6129A6 1.3 213331.]1 2.31123 . E. -IVt N 27.111 40596.? 2.11623 E E. 45 NxY M 190 ..44,50 44]6..10 2150606 III 213130,65 ELB ,) T 0' 105-1;i 405?1 2.Il 14-31- 1.. Ew x111 4 2052.}1 4061168.56 2/6351055 2 9 1,50 N1005'4744 1.25 .570.76 41 2-.2x5 5 RE N . I1' 40.5]1,]6 210152 53 54 N •34'i IF CiftlAD'ISIF 1.71' 4051-27 405.17 2.1S2A86 246]310. L54 -U&I M 755 IE9N? 2102.25 . F EM E% 4594445 1x2468,71 2151162 21191.00 -WE 1.3 4561693 54W1lm 6] 2 1101' .3551,}3 2{ E7 EN 2'11 f 86' 1011.1 10690.11 21112Oll 4 21556. ¢0 N ,2 .635.11 24113991 132 41 9A'1 4057616 214431.51 EN N 4oeo5G,lo 4016110 24w0Aro 206.9.. E1 E1 x '4 4611' 'E 43.111V 41.11' 40606390 40601074 2.3 0.p 2f-1380 E7 '6x1 1017.74 2x77.4 EN Em N ]N 41141},67 45151D 113 7 1 N EN En 40916,23 4G61]5.1 245 4140411 014 EA 1 t 146 .1.1 251445 15101,61 21.40. 21310% 14 It- .811.31 21.11.- IM E_7 .241 1 `E x>Y 4525- N. f_7 141 NISIV3YE 39,90, 45 1 . W.55 15 2-..15 21an.86 M ml 4.11- 21.51' 106167.13 1139,2 21 .1 411 1 02 15 N14WWE 3767 45417% 11/11204 N OI50 E, .41113% 52 21113)1] E5 10 N -51 22 ?526.W 2.4159 21160.2 ECA NOOI 18 2L2N 486 ,M %0 H ' ' E 3 Y 0 21-71. 4ZZW 246.12.1 23 C?aM 13 21-7.18 21419284 1.17.7C 7B 7, .8505.. N 11641311 34,1 " 79 EDe SMUWIN 51.1f .616% 41Nan 26x21 2140111.5 15 413034 5. Elm E03 1103 V?jV,3, s7s3+)2-W -311 01 15244.. 41x56: 4Ex2B17 2 41,1 1, 2.391. 1108 409222 215155 E11 aBi94" 21 1.x4 117 El. 45174,5 -IM 2-31190 31311. EIN 4115? 2aN41.5 Vic 6 ' .61673 Z 3)037 VI1 1E 35=1017, ci.,f 401t11B 216556.16 1 4 45N?m -91.90 .-1 Flt 4581123 21510,80 418110 248315 E117 W M 65 7325 2 0.1 1111 118 .. _ sall 6 6x%1% 2. N 2 410.24 f130 421 8610 -.1' 106 45111.n , Q-1562 3129.2 11123 12 N-0-111 -7, 406155 10611.52 151x, Z-.." 145 71.4 4124an 100?6..N 24-11.02 11611691 N 1'ZYE -eJ21Jl 2 ? nv 3 26. .? 1? '13 E -7- .If' 4I.QZ x13 2463471.31 Eft 'E 1 1 112i 7,32 -32 21 n 4. 1386 T' IOBxl.S l4EJ50.n 186 EIN 4545.'2 411311 x42361.1 2 4638 EIN I 40,10.03 .130.1. 2463701. 35 x.31.5 Ell El 40,519- .611x,1 x41? Z1 21-02. El. V0 wxwArW .637.60 .61410 ",.9%26 3.3,11 041 E142 EI19 106174JI +x14.1 11.45 213505.62 EI. EIN 72 .1 1 110 -41 4E611?n 313NJ- El- E -z53 21.4.1 E l- 197 21.193 fH9 151117 ?.NMN 1160 114X71 40!44x1 [131 E I M 4004043 4.x497 7 1 .1 l. El I4e3ass 240.16.? . V. 486 45550 . 210.4 7. 3 Etn 111 401NA45 41311 11 1 19- 4x16242 -ON -75' 11l%5 24633K23 EI9 1.1 U 41' r .J3. --II 24816672 263211 E162 Ei- 4061141 4530602 286 .- 2115.1.12 I-V .6311 434-?AJS El. 11 wIrIOW 8.,m* 411230 453219 2483201.16 ]1524.. E17 x310.47 21.68x2 E11 E17 -ww x62-.15 1524688 434-?I.v 2463241.5 Elm Et71 V617'52'W ..M 0632x.1 x6202.91 3.62441 2652007 Etn 4.111- N EIII 44410.7 4- 2v V74 Eno 1711 -2C 1 4 Y,6.+I 30.71' 40611LIN 45102x6 246 60 24-28.7 - LNE F WETI_AAM fCdN u-Fni FLAG TABLE FUG NO. BEARING LENGTH NORTHING EASING On 141 x9044 .. 24431 21 - F186 EI1 444921.98 105940.1 531IM2N2J 2 416311.. [i% EIN --u2mculw- v-, 91.8E x57% x6..65 2032%.63 ft1 ON 6.k-.? 444111 246x25,0 2534647 17 154.4 2130592 1186 405mm 21%11'9 ON E1 45i61C1 4a61Mm 240322600 246123127 1D1 4053571 212220-09 V92 -..78 RW1513 0J 194 JURILEw- ..24' UAV 405441, 105600,1 NW21.0 21)2141 N EIN 1558.% 105655,81 213%1. 20=2193 11 S2MWE 19119' 10'? Y.20 21N61. EIN EM x55090 405513.% 2131..15 215192.44 Em1 Em0 4054/1.}5 x./3.94 21 51 21110A02 E93 RN IDN40.it x.1247 2. .% 1 .i,C 175 w Mai -L--- 121 27.74 40015514 2-0]72 Elm E20E OZ4rM'W soivm*w -W +5nN1 ?2D0. 440.540 2405&N E209 110 .5214.40 x75.0 14 .2 24631611,4 f2i1 1712 .5101. 45117,16 24"0.. 24618520 1213 4511198 25910500 1214 1213 W4MV .- 01.1 4111156 2 586 EM6 521] 1 M 1 405".2 N .IAN 101115.27 Rla E1B --1 x1..42 24-II129 2031210 Elm 1211 319 ' >M IY M 17 4019.13 40.31,75 9x11., 113114.11 C22 10'40 404601.. 213102-01 E2U 4511. 2463/0113 .. 121 611 1' 463 x114.64 2 21 00x5 EV0 101 ,9 2 3 Z II i E2? 1 ? 4Lw 51-78' x4711. 10467393 P.JIDI 2.J 120 .173. . ]6 029 58'50'1 52 101030.m 2.31191 ON 430 E431 NY .49TH 0.4.63 21.512 246W/12 41=5 E2N .Ie510 401JQ0.1 21116745 21192.0 JEW 149 1 7 40146x% 901-8.5 246 N 55 2111411 RS Yx IZOD, 1..67% 213x,. 1219 184 x04 4043OA.82 24EW4 120 0'01' 61 0TH 14' 6. .19170 129.41 4 2".551 2 E1x AY M .12291 117.0 24OWZW 20.0203 21X5%51 F211 123 NwII CO. ,0111.11 0.U 2463107.51 2130/90 f21 '3.0' 'W 1. 1042 21312% I E245 &-sle W IM-r?-IN 236 .1 -4..43 axa9 240.%01 24x521181 ONO -M S 40431.- 11 ,.,,4 1200 801 SINIO'H-W -Y , -11 x4.21 .-Co 21325442 4136}1 147 .400.86 213181111 853 U54 NMWWW N'W N MIJ- 21.7 4045275 04M1N 2.31017 21612197 E25 ME PL ALONG R - I''232"W 125,64' x431510 .6x.41 2.216,1 24620511 AL6WD R PL 09 •W 1 r 4.x9.4 4.8X4 24621173,04 2464887.7 E2B 40x1310 110?B135 1260 2E . PL -PL Y 1 404221M -1217.00 4402512 2027.64 -, NI Y 'W .4104" 2121051 ALONG PL 1 1.96.31 2.27131 AL060 PL PL lE 0 ERN : Y N 1 21,81' x40186 x1610 10?00.Do 2/ m.N R- ME R PL &06G PL 10120.12 10181.% -- 212155® AL019 PL N W ft.M 4,mz1 -.51 !1069 PIL N+' 4042'6.1 2.261 ALONG PL ALONG PL S34151105ow 113,71' 40420,9 x42 m 2.29814 2102399 ALONG PL ME 0 78 N x42071 2 0 1.2371,94 12811E 0 PL 434 1.11 20Z337.0 ALOAS R " ALONG FL w MS 246%410!1 AL01B PL 'PL 1E MO ENO 1' .-1395 1041951 11924202 24-61 E30B Tk 401 PL ALONG PL x NOr4X47E 7Q' x111.1 101540.. 7 . 24S25N ALOX4 PL ALONG R N 1 n MIJS01 2022510$ 211 291 ME MG C., 1 40120.- Z.ix5- N1 ME m K PL E 7 243 7 ALONG PL PL SIB TO )19 • E DrM N 40497,5 260 2141/651 B 2.=..w E €nI 861 -4-- 410d .411.05 4x5922 2011.1 2402190S0 2 00.18 -- N ro PL _AjQ2EAy2_ JIM' wN1,11 5. A1d. PL PL ME 027 N-21- Noeve-w-w 41.11' 57,10' 1250522 45130.1 1.71 .84 2121151 UN] 400187.40 x-10," 132 105244. 2100230 -2 E20 R ro PL 405219.7 405367/.20 24021- 202062.- 9x116 PL PL ME 0 -N 45341.>1 15155 21X.0.9 202x16 EJN EIN [07 E - 101 2 1. 210. 1 ENO Daw 11 09.51 N 2. 200807 E,1 D- ?4W. 4(9114 205140.7 1155 1182]0.4 -N EN 4.568517. . 4011 21951 F -IT 151,4 201011 24092.13 24/20112 9']2'if31 .IL'_ _.5=1.51 _-201 5=0 21.6748 $5' x570193 2112964 1250 101 105]x10 01,24 221"4.1 2449 A 6.5 ]124 405 G2 2181 ,1f 2401112 -X5 45]40 405817. 2x444111 911931 M ENT 4051585 xs1]n 211D445 211.0x0 E; 1059514 16}5164 11 ME 9 C0 135 -1 -WWW 4064 1 4.191. 4035}611 14106129 2411819 8141211 FLAG TABLE FUG N0. BEARING LENGTH NORTHING EASING 415 rW 11594 .67x0.2 2.15!1.6 x301 . 400.x5 1-7 003 TW 44' x312.0 4x402. Tea 003 455 10715.5 zum5l,x 2x191? i T=OT 'E 7,55 .,10.1 .614111 2x-as 2.215 TJ5 wnMES 25714&. TND TNO 1311 4' 'E N 2 .07.5 .4441 404021 251721 Z19xNx 2491x1 ?II FLAG TABLE FLAG NO REAPING LENGTH NORTHING BASTING RP9 3.1@lY,y 4' 40749- 245x4,63 1x0 802 Je,l' wIfW.12 .43,22 P V .13 245lCi.10 R2- 40111511 -C.D. Rm2 R205 w131.N .61.9.5 E {1 P1xx1 841 42-,1 I 111,W I2 840] '. ai71x 245101 NorazWE .0x442 x4,4.1 bnmOs 11-02 RN11 4002x. .1325. 2x455. 215x5642 Rn] 93.] -WIVE .}2565 .1311.9 243x01.32 2451810.15 19 x44 p,2 ,PIS a]A10.19 1"1.35 121 1217 NII - .1x52 44415 26411111 21540..19 8219 w]4Mx :1111..675 8219 1?0 -wVrg NOI 11- .011144 .14.. 2140-n x21 .i-1.39 u119.n 12 .740x73 .0609680 R?3 821 OCII 24011,4 x739221 }x405,. RP26 .6135- 243x90." C.. .)5>ffi 41.1601 RRl R"8 w>N3.01 .6131500 2512x5 2,446 R4? 1210 863. 4204.}1 247121]] 2.43.1 8231 RU2 " " .38583 135 21101. 44.12,1 820 .1340" 25419.: R4. 8215 111 .67311.7 401 N i. 20" 3 RxN x10 P w}.0.51 2491651/ R237 401'AA00 41x1.13 3671 R f . .41.18 .TIIA.ii 21.901] P10454- R2. 2w R241 -?WW C1.1' .1x-,1 .4111 2315"44 2 - I PJ1 P311 t 4048` 02 1,011.93 15 211-46x1 2x11 P311 V- Q7176.03 2AN .. 8310 M .7 .1 M PVS-N P.NR 4300 Im3.0 ?725140 1 4. 254351.41 I 7 M .131140 NN071 " M M .10106 245401.73 1164?529 91 I . .149x8 -9.115 -9.115 . 1-'17% 145430 LNE P.T WETLANDS RAG TABLE FLAG 40. BEARING LENGTH NORTHING EASIING PI 11-41'1- -29 .1154 24551.51 % P1 NOSU12*W 2%02' 4GOI 4011.2A 24551.11 24513,? PI Pe x1/11 4015251 2491443] 445511X5 P7 PB 4.31 x1111 24617.94 255044@ PI Nwullw? COL., 540,03 1043 11 PII 41412 21E5012w P1x P2 -W?rvv 1211' bA25x x4560590 2 414 415 -111-1 4081.2 4441.5 . 26.x1 24550-54 411 PIl 2W 9.3912 906.6.12 14514.1 2a544p. P1a 40635531 25 PI2 EL IISIW3? .26 27 10-591 40831x5 -Go. 215519607 PN P2 4083127 24552255 25526143 P2 -W?IE .%' -w 356259 x5?25 252275 249.60 P2C .115894 x1651.? P? 412468 2x5.1.9 P21 P28 19' w 1164 .82].86 849511 249]]21 n6. 0 1 Y X MI 45191.5rs .161.- 25Nxa 2455.6." A n .-W 6' M - 10. -'al, lGNDan 413.22.5 11-.52 0 2?01J 14115= w 7 CY6 4011744 24515431 l4 i4 n I,VOCI 1 40-2}.61 40I0C6.1 2152404 415525.04 R T 'JM x '11.44 I' ?l .1 -.00 15.7.9 24 24MI5.S126221 0 LM 7300, PB00 WEFL.ANffi RAG TABLE --- FLAG _ BEARING LENGTH - NORTHING - _ EA5NNG ' 1+ 31,4' 1 Ow 15 W10l" 2+K 9.V 21Nuz. .,r 170 9 - f IC .. .7157.94 4041.10 240151 2"41-. 21616394 -ONWE -W ana6% z4e11s1 10 4017M..N' 29]N.an 2112]9 % IL I. 1-. - x123144 2 266.46 09 206205,46 X+E N 1'I i a 1 2446 . NI6 Kn Y I, 07= 16 x}}37.72 4 61 2.3361]5 a . 1 Km 4012.]5 31.x.1.1 K21 Nowlirw 41,7V x131,9 2412,5 . 8643 `x 36,18' x229944 .7416 x.644].41 4.6 '8 K2 K xteel'sf'[ -71 .7N1.90 . 734101 2061 2 . k" 6730013 2x6230.N rc27 562xae3 245 Tao N .144aN .217!.4 2055 1.9=45111+ -9 .147161 40402 1 6 4.9251 .80 Kx K0 11 AV 76. 91 401451 245mB.x 2.6 1 .2 KN ' 144 x751.21 2W211- K KM .611]96 .)921 E4NI.m 2154427 17161- :4114.. 9% ._W 40TH .]11.61 4.6}44. KN N. M .M k' 40251 x416. 241140.. 44111x. rc1 862 'xrW 14'.'0 7 }r 50110,0 x46].11 . 1 J,86 2 11 K. 404492 ",N1G,a Kw 23.27 .414.- 4.6013_7 - _ S9'Je'24'E X59A5'50'E 1 .1022-04 .10.1 7 241..4 29601?: I RF PF 10 18115 FUG TABLE FLAG NO. BEARING LENGTH NORTHING EA571NG PTS 462861.x.3 462-6.16 2x18114 20n71 n] PT4 N--WW 4LnkL 11TH." .67122 1451Mn 2x77N PIC -WW __ _ w IV 407931.57 2xnlaa2 PO FMC % x1102 2x7581 lx 1 403154.03 21730112 4091203 243111.1E 412 PM5 -51 5t 2x)110.1 2437360.1 PHS 1116 .-wIC-W ,.w 1 40&35D.93 2x67.594 294 Pit] Pnx -by -4474 165211 ]J 204372OL4 245115.09 P f9 2x7125.30 PM n0 4034..01 2x71441 PI'4x 1 47-7'91"N I.M111 40.1112 -416.12 243 111 2170101 .3.3 1.4 N+wDWwW Y .6444X5 2455961 M IM .% a9.m 2x11141 2x1129. .. Pne we52.e2 2165917: PI .-44.86 2455611 PIN J4 4004161 !x1101344 1rn ] +o199.m sxe15? nil Pis 41-125 96,'5,2 1451-15 4x116961 PTN 419 Y eN 400594 201 257a1 411 PTN 1 . e 90.]11 Ex05e,03 7 n6. nx i 404.6770 5 E+110. l11-031 LIE P 900.T 4100 WERM96 RAG TABLE RAG NO. BEARING LENGTH NORTHING EASING 405 491 4118161 45113. 26. 10 Ex52.N P032 4123591 215551." P95 40n.G0 25510.- P05 PP057 N2415-48I N.Ce a%7% 1128205 2.125 P1" 1 108204 21%4.1 PIS 4080 I 79 40-X552 2159.2 E15.BB-0E P11 16651.22 ",551177 PN3 4[4310 251277 96 1 4C-55 40815269 45 2IN 4155O0244 s PNa 4+16.7.64 4110.2 21551494 -24355144 741 90512.. 2135155 psoa --C7-1 1-1 4055797 24.551555 4969 405199 215.35 2211 PD71 40615510 40.2222 215N6n 24973291 22 40311+.? Q17wJ1 PBA P974 CI n3y 40910.63 .72.75 2x57.522 4456 N 447. 1517,89 2512.32 PB7. 4011 4 .9J 99]1 401 x N .0 994 MM171E 11,14- 151 " P975 nw- 4094.3] 2455900.1 POn PON 405009.52 PI1 X10 Illd'JG9.0 PB0.1 -AIII +1]67 . 1015.. 1 41 P- ? g IOa057 24551.5 T4U t Z 109." 415523] T42 11 2Eri3t 1.1' 1511. 407809.03 3411%1 11.05 210 709 71' 4047131 40716.2 Q4519.]] 24a611.0 2+0 r1 40]4401 1.32.5 a 191.4] 21551.x2 -116 407M.18 P IS 0415 x715.1 2 % 14 To 271].. 15 4 31 Tx1 N 91111-01 I1 a 40144 x484.44 5 345551 Iwo T i . 367 b 367 9155E0.n 2167444 ., wl 045 x 42259 .7951 x11n49D NSm72 Tai 6712 40806217 7 245535.18 2455813.32 T 1K`2 .1 4515.,2 21532,. 145550.? 006 I' 16 01 25 1514.1 4 AN PIx52u NO SCALE LIE R 900 P AM P2M WETI_ANnR --- FLAG TABLE FLAG NO. BEARING LENGTH NORTHING LASTING RUG 406516.62 2x4715® X51 109538.20 2x473609 A5ax N. 547991 x503 x 3'.'Il' 7, W D 2464]31- Ras 1 ' .86 aeuo. - x 44 R5ae N 7.2' 4O914.1 2x02416 :x.5566 2xN5G.4 R5 RIND 1' 400641.75 2x286096 10 8510 x5.45' 944741]5 24.911111 Rsli DO 61, 4@]6,51 2x195618 ,512 --' -4' x52114 24316.65 ,513 E72-W31-5 4V_ 195.8.24 4050X33 435 ,514 109521.49 24557.85 815 '6Y x11.1 IN.22 ROD 1 408078464 24%161.21 ' 2x5:06.. 4515 slnvvl? 36.2C 40OP SO 3 2155231.54 R19 OVDITWE MO' 1.43 .. R5m 10861218 2x5272- R52 7' 401334 2 n5 R612 8524 40125.m 40860792 2466216.. 215346,64 875 8516 SgLaff 4 -M' -' 4084x8.. 41-37 2155353.40 2454.75 ,627 1E 10-83% 24034-.71 979 NOWDITN 4051073 2 - R3? 406407,07 245x2- ASm .8x172 24.441 R5 m w 1 165 249:9162 32 852 1M. 50 .- Z455J27 F6N I 19544`56 249356,. RSN .1e095 2/55215 855 N .9' 410121.35 212547.15 R536 -41-22-0 4096-% 2x55.91 R537 144653.0 2/5393.02 ,535 RSN N 40583190 .186% 245541,0 245161. 150 -WwW x116944 2-C.7ID 36.1 WIW"'W 11 40072596 246547367 R.2 R51J 311 1. 1189556 . t 142115.9 RS- M 32.13' 10e8]02x 219307.1 R51 r4Cw MAV 5164x0 .531.+0 A5" N 1 .68 04 14512.0 R64t 1 ?? x91,.34 x5551.44 851 241:.'49 4087x.4 2455187 6..e .. 'W .14x17 2462x" 850 -1 x164 21521.1 F551 N4sl2V"3'W 51,18' i. 2 55123- R552 -4 119x123 4 2x R65 5 4191.. 245ln2l 104.14 ,551 - 245510.77 1 A '15TH ]. .9215 24190.57 x16 A957 300' 91595 1095492 2.W7 215 l 15577 Am, IlCYW. -, 40051.37 a2I22N 24111.0 2111x.% RON ,560 M.W2VIN 027' 4.1951 2x514175 3651 4O914.114 24 .1 3653 N 1 '1 M 40027.% 00. 1451 75 813 % 2455009.19 8584 R503 48.40.2 545110.1 R 1129 3656 -. ' 15A4591 2411115 R607 Na?ww -W 1001401 E 10621 R10 N 'W'W x ,IC 245500&26 A 0 R510 .099 ,57 401112 2+554.. 24515197 8371 R572 N -''IVV NUM'WE 1 4551.92 4091 44205.2 44511173 R573 NC-1ICv .11, N 215M81 8574 4509? 2 % Fall N 401767,1 21660$172 875 RS12 40910. +.0214 2x189% 2 B -71 40911.59 xbIB22E0 R$79 -T 45643.23 246072.25 850 851 044 -CY 4 001 1095 1 .519.52 2 852 IM3 S05-42'511*01 -4W x901 1679 x15 2xI619.92 2154142 Rw -XICT x925.9 21x47,35 155 R5. -4elm-E -CG- 400165.0 407542 25-91.31 2W 09 Rk/ RNO 400INI 4 Nx.S 24391x11 24551.7 RNI 4091,7 2.519.11 R503 Itl. IrE 7' x0557.11 40NI512 15 2+5491.60 8585 M x2519 2455100.00 455lW41-W M 2/501.25 R77 -MT 1171' 10941.33 2651036 8245 400361.12 .650526. 8598 -WT 40-55 2x506473 ,800 40001.75 2199284 4130 .99.9 2.fi0-69 129 . . - . 2x529.57 PM a%43.57 2-9.00 421 41 x9202 29,67.. 426 4225 51354'0] x97]0 49107./2 2159.,72 255174 P24 13, .946.85 2154x31 25 . 2 N 422 865 8' 2.43 x890.0. 25155.0 P221 Pa0 slew,57*w Ism' .9.101 40492141 - 2110790 P219 10915'9 94.7171 P?8 .1' lO881 45 2464950.72 P J 41- 1. 14 95491 P210 .11.5 2-.1.21 P 5 P0+ .571.2 .14 245158153 P213 N 1 405762 26 2 x19 P212 N262r4V'W 108152.1 20x155 P211 x5.1.? 24611591 MID :910X5 2.54.- 427 401196 24.752-02 495 Pmt wwww 2 .6'110.11 157.1. 2x140.52 2-9190.5 421 1205 M I x11792 4006117 2-1712.5 2454691.. P204 x8602.90 2.75. P203 157,.5 258119 P202 W&.30rorE MAC' x7152 251.03 P21 '1.43 1515% 42.2 `700 W x575569 24.926.73 P P301 3.5 ...... 1081214 09 245410.51 2.01 P- NJOJSNW 12 2..442 P303 -'2r. 26,43' 2 46UR 2x5%44 a x ' MN x24meE 1'M5SD1 4- 431 x 5173 21445715 P J 20,731 686 2x458.4 D 10 .180.5 2454647.04 411 Y 401x62 ID 2x45-x PJI2 419 61 J J 581,1 x4545554 4511 432 .055H3119 .660,5 2465C118 v 24.5]552 46hfK1V1C71.Y,EM 243 NORTH FRONT STREET WMINGTRI, NORTH CARO,NA 28401 IFIE `910 313-I'4 FA% f 9210 251-6281 hlty', //4407 dlmvee0[Nn LINE P 400J E5W WETLAEOB FLAG TABLE FLAG -40, BEARING LENGTH _ NORTHING LASTING Pao Pal Ni 41202,11 412.1., 24.11.4 +540639 P402 MII'52'E U.71' 41215: 2x4lzt.a P402A N.VZC'IVE I-1 4144417 2x4113.5 PI- 412072.31 241156.97 PE1 34502,13 PS P12 I' x19651. x192140 1x415.1 21415n P5p1 13TH T' x1-14 14.149.92 FLAG TABLE FLAG NO. RI5 BEARING LENGTH NORTHING 4-1fl9 BASTING 2.511111 R)1 I R ED 41100.10 4-7N.N 2455420.69 21.111 4103 S27' 5211' 11.11558 245516715 R]N Rm5 wowo- 50274B'22E -2- 0,W- 4f-49.14 414.93 NBk55 215545x% R7M 1111 so-31,50-W DI x1452% 41-509 .5915 2155120 IS 8108 R71G '"'S { 14x.48 1- 2553n.. N.m I 8.42 i 19.86 R11E R713 ,63 I.k 2154MO0 nll 716 3.61 2- 31.4.2 2151221 1716 4717 'E 03 3. 1455449.31 2159.1 8116 411 21 ... R719 4.62 245556121 RYm NI ' •E /4,68 721 8722 5 100 246MM 215..15 1.13 245565012 ,111 34 Al 2455701 Rn5 Al? R71i 1 ' 918'05'1'40 414010,15 /+}41.5 }811.40 21x01684 .45510.1 140.955 LIE R 400 VI ETLAND9 FUG TABLE RAG N0. BEARING LENGTH NORTHING EASING ,400 11' ' 411.1.89 245121.. 1,41 Rat Y M 1109.. 4131161 2 9 137x3.06 Rw 'a {1-.N 2"167.1 8101 N72-4W17'W 41., 41 x Ras 41311.67 4500.70 R I I' 325177 4116522 8607 01 -W'l 5J.37 . x,7291.7 258-.74 x401 R98 8610 -211 N.Irww ODAV 0' .. 21&f- 414-1609 1NOI.N 41525.75 245398.14 24608128 26. I.n R4N 361E N1J N E 4. 5 41150.31 7 11061.87 2xll10.18 96 2054.1 NH N -'W IIN0791 1 s1 25337692 Pbl.3? Ntx N 413772.5 245 R41] 118 41]]5x4 41= 9 W 2403138161362 1"011. WETLANDS DELINEATION SURVEY f 6s) <y FOR ' `r WEYERHAEUSER REAL ESTATE E,e, t DEVELOPMENT COMPANY o i PORTION OF ONSLOW 19 TRACT y, RlWAADS 7VWNSHJP -- ONSLOE - VORM fI' ROLNA Juna, e Z9, 211, 20 8007 NO O SCALE SCALE PROJECT 4: 0 100163 PRIM SVYA : DLJ DRAWN BY : AGE FIELD BK. : .67013/56 - LJ COMP. FILE : vN101-009100163-2 SHEET N : SHEET 4 OF 14 DWG. III LIE NB00 WETL4F479 LINE L WETLANDS $a Yg N LNE P wI AS TABLE FLAG 570. BEARING LENGTH N1WxhIING EASING vi 10]011]4 205116.16 PJ w 419..0 101891.1 µn0.5 2.578.16 1686µ,U 2651431 PS 4.1214 4681461 1658.16 3 .i4 Pr 4.1451 245150 PB vB 1.84176 4.176. Y 71.1 1 21 P11 PI2 1061.E1 111.1 21651]0.9 211115.4] PIS 4.7123 E058µ,1 PI4 1._..41 - 4pf 0.M 10,71 1µ8113V 20111132 117 P1 1" 4.65.1 2111 ]4m5µ.11 1611.53 . 1.714. PIB 4.0.010 0/141.14 .Bend 2.5154. P22 wffir.i] 06515n6 P23 PI4 940- - 166412. 160µ).n 3 4.4 P3M PS wv:wl3lw 1!1534?'31'E 189" M86' 4.µ1.m 4.11.1 2µ763162 3 w 42716 20510.. P27 106.8,0' 206509.1 P3 P. 4.1681 109.8. 2.011.82 2185.0.15 P. P!1 92 14! 16Iu m x41/ .20 PN 1682-1 w8n7a 20&50,1 20x0&. P. nor 4.1.31 E451911 168124 .3 1068117 w 4.1m.µ 21651..14 P1 Pn W 4' w601.u 16 wn 20 1950 242 Pa 40510.1 265]141 P1 Pa %7WI2'E 4,78' 0. 41x7141 10690,14 2µ81M50 w 4o1a.W 176]0.1 F4i ' 'F 165051 405884.18 2.6121 2µ9681m Pµ 'I 405989.1 4111.1 1412µ14112101I 1 Pw 1 w67n.a 4a1µ.62 2k191.. .1181 1. 41)0.. I416Y6a 419 4.61oeii 2µ1n P5u w 1.6-..b 4466 451 V. 71.26' /0552691 245-119 Pm N 9 .19142 x 3 2 0 484 Px N1 017'45'W µ 161x76 20x321 P1 w I-y 14ISMI- 1 w 451 P1 N-T?elkf 1,175IN-2r, 15.1y 2"r 10]01.14 x211 24557618 40180.18 Pm 40127.97 4.111.14 P. Pm 16!109.1 n. 110 !.91 116519.1 491 PoJ SN'W2,131. 9 11o., 7 7 2µ5518a 116 .0 Pot 7 ' W 90818.,01 20 111 4111.xi 14811.07 Pee .a 5165-t9. Phi a 2 1 5 P1 469 ?,rm*w 1 slow 42-811 2163110.23 2µ19951J Pn 11111413,E 215o' 4 m 24"W.37 P72 Pit µ102n 2µf9-.n PIS E 16583,0 10516]5 2161.6.. 20761680 .15]55 2.501101 P . R2111174" Y 23,881 10%16.8 16192.31 2051725 1166761.14 n! Pn 4.1421)11 2 5 P1 Pm Nlfilw?rE _ss .17 4a11a16 16161. .76& Eµ.]ax 2µJ181 16.1.15 24511961 P1 Sjf?V26*W 1611,14 2051M.61 1µ5a531 ,n P1 1'01' 156-3 711,65 10.0.00 20.34.1 Peg 11 2µ'416S PW 16116,. 1004.1 491 PA2 493 y w '1416 a1ma 165514.51 76192.1 E000m 2464.1.98 145103,74 494 '14r. 16x1414 4µS,111 4x5 9.-J, 21901516 1614 165w9 .µ a PBB ' 1 ' 41.71 10615291 Pµ430.1 Zµ4n8m v1 'I x V 4.490 11 2047.4] M ,142 7 ' 4 I. r -11 11 16-5 201 m 2w1M2m 411 4111.44 1µµ21.w 1110 1110 40x1898 1118.26 m 2µµ..0 1113 r ' 161771 2µ011A6 ,lit 1 J N 4 ' 11112.1 1.590.0 2µ I, 2076 m 1 %14 NII52rorw N-WE 1. 4."]1&14 .6503 02 216.1 26µ1A1 %1e NW4r2r, 10,14' . a5m552 z ee %n m 1668..14 .. %ie P120 15 n5y 1o117w 16118. z 1 1 P120 N1' 1 405168.18 a . %:1 N-M-W 19.15' - 4osle,n 442 PIS %U ' 1 JIM 100101.94 0 1, 14818&0.. %24 NM- 27,77' N P1a +011.1 :M4aao2 P13 .m 11..116 Pln 1 IOCWI.M 00015.90 Pla 1121 1663x.8 4.842,- 104501r4 2µ41S17 ,170 Pln SIOW50, .. 61,39, 41771.0 _1x50 16010.30 20µ11.M %a gal: 401.16 tw+e1- %3l 165x876 20437. %34 %m 1051E. 23 1.1610 471 204737.W %a 0 %n % N,51r.,w 20.2e ..111 16x162 =1 4 218471781 1x5 PI %a 1p5-1 511µ ?0Na15 4111 %w 716 161214 a 1431 1 n 11 42A .711"Wly M73* 1.818.. 411118 M 216 PIN Mir 16611898 1 6 %w 76400«2 1164.716 PI4! 05.1)1.1 965901 - 1016 1.60 01641 pi. III - _!111.x] Y1H a PI" S, 41021 1144 %m 4asl,en 1042 . %6P 4a53zu 342 n. I % 117 241410.61 0142 :155 2 11 4 6p1tt 46mffin 2 I 2.18151 M.BO 111n.x 41]..13 2-21-1 216421)M P16 05180.69 24.4121LM 162 1 4193 p 10184.1 409on.0 104114.81 118433,. Pia -42 1 m w 2bµ19.5) %m 6 . 40ao2- -17 14011Ami 0 Piei 41010 0.4µe3 PI1 40550176 Pla Pita 711 a5al.w 411].] 2 W 2016}]41 Ptn 4185176 20111.. 1173 1172 1M ,-n7* -yR2E;p_„ -MAIL.- --,fi 161) 1.36 41140.18 414113.x1 %14 161471.. 014111.41 Pi)5 . Inn PIM n 4a1- Din 4.x1.1 2 1 %n 40...41 I . 9 %n 4.x1.11 24.4]1.1 Pfeu 4.412.0 21641.. 111E P w nAN78 (CONTME6) FLAG NO. %BI Pmt P1m 15 411 Plm BEARING SsIVIVI 1 RAG TABLE LENGTH 1 NORTHING 169141& 16916.. 405371 1652µ,5p IOm 401721 LASTING 2µ15a.1] zuuze.w 2µµ26.n 216µ)1.i4 x16428) 204411 PIA] pin P11 %76 PI91 %92 %1 wmffia 16511759 165.514 44211.. 4.950.. 1616814. !768081 10414&1 2M4111- 916/11112 1µ1670.5t -3K4d115 24.01053 361. PIB4 P1A5 Pf9/ Rf ro FI 4..581 1046461 47634. 118.14.3 2..61.4 24Affi57w LIE R Wn ALOA FLAG TABLE FIAO NO. BEARING LENGTH NORTHING EASING RI n7111 WDE 415597.16 24%13165 R2 -dOrP 41%10,42 24u11µ R3 93, 05, 41554716 0x31.01 . R4 41556Qµ 2.21.48 1 425 _S57?9'191E 7719t), 415NSm 24542,5714 Re .'W52 L 4w5m.u 24x1..1 qi 41502614 24515211 R6 41x42- 01314.3) R3 1 41966.19 2045.,. 10 R11 N4rW'IeE 46,91' 4534k11 415311 14x31161 .61316 .1) .2 humUn 1.1• 41 90 2047n.n 13 Hlsll'x' 4154Rnw 24510116 PI4 11541,22 24101.16 RIS 05.4.10 200138E 116 134' 41x611 21545014 817 alxn.26 E1616.,n ,H8 41502.1. 2/.515.42 it. .11.05 1µ451.29 R76 41x2239 245..11 R21 812 46'0 .i 41576.19 41 14.1 1 M 24060100 RD Wr43'03"E 64,62' 115628.79 11&4624. IQ4 --- ALAL 415µ7.34 2µ4m591 RS stwaWw .-St; 2µw99.74 m 1E 042.0 21546x. 1127 14943,. 2M. j7 : 876 R3 R. 415m4.%7_ 415]4211kt 1151{.14 245161&. I 2450193 2µ47I1. 11 I' 415µ4d{ 0x115 Bn R0 ]R 03WIly, M.46' 415412. 41MIL72 76551 2wµ029 RN 57.16' 415N9.. 24.125] R0 R1 I a 41539.55 24516)094 245176061 RJr Y 1 11!1911 2-7.. Rm • 41UM..81 2451099.16 RJD S W 4151nPo 20481x. Rw m 50.10' 415IM91 24541.31 841 RIl Rµ d' WE m3y 061815 415.951 414014.. 2µ16i0.69 90161551 2403,n RM 1 11.1 414991.0 2454237.57 R45 1 059 4{49. .35 20µ211115 Rw N2121"Al -- 41µ25N 2454)34.. M] 110]43 2µ4OSG Rµ R0 Y1'E 410721 11µ0µ 1µ01n 49581 . 421 41µ11.11 3µ501Q9] R51 11492175 1465.310 Rm 414911 2451.46e R9 I' 415)1,91 2µ50623 R5. R0 Nurt 52,73, 415.o,u 4197919 24-.10 2465153. 16 R57 -26, u. 415.6µ 411.5.31 -,- 246199.51 R1 r,451WIrE 21,111 41496521 2452..44 no no 11410.89 M49S.a 101114 2/55]81,. Pm RIM Nlim'W" IMS-5414"E 15,00' 41490].]4 410.160 21-]1342 241676.'3 -_1 N 2195m4m 14 m -- 51'0 11.11 Moo, 41µ71a5 41µa13 246S501.42 21.394. "I R67 W-46-51-E 1 4102660 1102211 2455n781 24/411.93 R1 1113' 81411.3 2/141085 no 414141 05Sµ1.6] 110 > ' 4.17.35 x41414.1 R71 Y lom 411680 24:950 ,U 072 RI) 1,— 3149 ,1' 1I n 1161.59 2466µ0.66 2µN99.1 R74 Namule .is, 14 4 ]1119510 166 114 2µ5u1,92 516 R7 I X32, 414941.61 ll1 111 24 2/SS08 R 0 1149750 2455649. Rn 4260 N3n4'57-r 51 m, /1/96420 414%.51 2 2455721.90 P.I RU 41.4.11 41.659/ 9159151,1 4914. 571 II 9 2155 a Ref NZOWOVE ulay 41.6232 140614, US 08 41W 4151351 0 4414 2051µ.N Rm R1 N3I,3iIWE .9s' ll 4151MOO 11511u 2415iiAE2w 24169604 R. Rw a 4152119 5751138 246154. 30.371 Rol R93 10,16, 411.,24 1407661 24..a49 Ra Ra 572W14" 1- 59,12, 41.2436 415411.1 21..20 24.114.58 R1 415353,50 ]461... RVA µ. ro PL 0531].51 415.717 ]40.6,19 216110, LIE MOD WETLALA8 FLAG TABLE _ FLAG 570. BEARING LENGTH NORTHING ASTING MOG1 p 4.19 18 uou471 ' 4)42.;4 .480)1. 01 NOG 41u9.1 4MS1a0) 214 111 PwE- 5901 -hQLJIZQX 1.0 200!131 NOa .11µt4 .80592® Y • 'W 16x8134) 24w3n.87 042 .076 MI5'3rWW 37,W 40019] 1 100.161 0-310,31 7610 7 ] 111 04214258 MI" 4.rn.6 24-" 012 0413 40.-,99 161.16 200.WI.W 24993 590014 N-80.95 157.]...8 lOClS 1 9.04 0118 !52 16}x219 2em7 Y.52 1p1r I 40.91,1 2.042.. YpCl61W E W ALONC% lw 1.491,. 1664170 276.1.14 211618. DL PE w M01 410.78 4450)11. LBE Iwenmm FLAG TABLE ?._ FLAG NO. BEAAINO LENGTH NORTHING EASIING 1115 1442 .13671 4.5121 01 01552 201)12 41] w 11103. X12 1422 201101.27 Ifn 16818.. 2µ1141.m - In0 4.1055 2 1' 1676114 211.02 Ilm r I 1101.5 0611]14 111 140 26 .91]2 42.x15 4.a7.µ 2.108.6 2013210 x 2131 Iia 161951 1µ114&l3 1462 1161 10-)$50 1.1 Y4101a 201mra 1181 21,57, 12 IV3. 1150 4.35. 2 1418.16 1476 401220 P.143.94 1 n 1 OR 105/076 1466 IM 1 2x14951 111 4.2.!2.66 2µ111.6A 1151 IIU JORM Y 1614191 4.11,24 901612.00 9µ161S69 Iml 1681141 4164169,1 11w 40111 142.5)1 201111 10100.73 uM 4142.1 :ut454.73 1141 1116 4)14x0 16141!.98 31141. 091µS11 110 1' 16717. 21B1µ149 u. I1µ 11.1 16.883 --- 4100 2481476.. 1142 1141 1 51 167 b1 H 201+t7W 20143259 I. Slsulww 242.5 4)143.17 40145161 TIN w 16.1' a11o1.16 24142216 111 3 .1 40111.30 24-- 1137 161991 .35041 241 z.1118. 1465 w ULM' 4DM10.u 20139.1 140 X w 4DMI_ .16-57 24101.71 201291.,16 1131 1460 'N N1 ' w I .18395 16190611 20111.. 2011..5 113 11W X X 16)11 1677371 1 11 ,. 246141,6 nn 17 .11 1614.7.- 201176.14 1476 II76 41 -7 wmau 2461 .1 a.10610 1424 w 1618101 361.116 1143 1192 Y .711414 .14111 101001,1 590.141 111 w1µ8.95 0 arn6n 9014 111) 40m].µ 1.1W108 m 111. Ills 40n0.71 w11µ 1115 1114 IIIS $671,V2rf 29,10, 16.76.11 -mm M2 1112 1111 w11am 4)76..16 1110 WIIW4.r _j=L_ 16711. 10IN3It t I .1E1 µ I'm I&Iw 16110.1 1 JS.11 '101 3142 111 a111u 1615&.53 16]76 01 3111011 Ew1 uG . 1611651 4.1-1 0)181 z.114].1 n. not 6]111 16742.0 .61]00.11 101211 nm 6 x 1 ,. 1f1 10 l Cf ` 161486 1674/1 20101.2 2 I 114 n " 16.1205 1611 m 190 4 246114520 lµ I. 4) I M MWI.67 161401.6r 201216. 201 In w1nEu =L. 2.13120 141 190 MVlr37W 66,M, 01153 4 2.1311.1 14513121 11 S51514?05'W 6855' 7Mdn _1x1919 61310 116 1 a12nm w13N,84 P01-AU 2461261.25 10 la 115,W wI21Pl6? 9w1M..u P.121,1 182 ]m µ .01.13 20114144 2011120 I anon 201 J1 tm 'I' 1671..1 10131832 1 w7t102 41409032 20114107 1 41612911 In I16 1159, 161.4.1 1617661 xMU16w 201x9.. 145 0701n z"IJ101 04 173 'w !AN 40111!,3 168.524 N41TIpw 0 61) 79 IM I. 11x' 3 .16' 101911.4 /1114.24 E.15116 407910 In IAA ]x M 357' 7615)5 4 101114. 2010144 167 IB 1 .-849118 = 20101.0 ]µ161.w 0 I- ,ff 1 32 16171352 2 1/ n 20176 01 m -1351 76 .1 2.10 m .10x1 p: .m 4.143.4 .142742 0 Im S-41E 419- 166111.0 161411.10 25&42 2 1' 166160) 11-1 2-0151.61 I% 159 WW'43'E am, 12681 0811 62 In IN I9. 9 16767 . 1 4.183. -- 1.1.816 Im 4 40130.63 3161.1.18 lu 30. ' 41-194 ].100.10 IU 151 1 4r *14557194 4111.1 20fµ0. 2e14141 .1 sx),3m WE 4.427 12 W BO 149 m1w 10 L 2,itiM7112 2µ1µ3.1a 10 4117zw 1 571 1131147215 4.02.5 zuuxel 1160.1 u afa 14-461 1µ 4130.16 94111 1 2414!1.26 593 111 3.1143.16 4.3042 x 1 M In 11 1067145.. 1)0.11 201... .63 2.131214 .w 201].1] v !M 10. a 442112 201611 7 l I. n' 16190. 1.&111 2.1l9µ f4µ11 In IN 1141 1.912. 314)1 918141541 3314 21 b 4. 10eI..eV l 1511,19 la 119 011164 f1z3 36152&. 20111.1 111 rib %111.1 16601510 20114. 201&5946 126 4.044.1 241.14 r I. 123 - a 405961,87 016912 ' 1 b 322 16391 2 1.3519) f1 p0 17 2 191.31 2161611.w Ii9 4.14.1 Pwt d 8 In 161750 -Wa. 01140.. 576 4119.3 IM1iMn 145 165.1.. 4261 Ma 1E6B1p1 101711. 116 l 7614)0 ! 4110,) H81n8/1 P00µ4 H 51 9 411319 ! 20110633 ]IO ..17.1 1 1153. 10. 4[1"91 le m mll x611 . 11 7616.10 1.314&99 le m 4.514.. .1t 416, 14 To TO IL 16151.1 _1..10.1 UM WE VIETUMS FLAG TABLE FLAG NO. BEARING LENGTH NOAiHING ' EASING PL TE ro i 1117 0 x 7 . 405 4261] .0116] 9 1U11661 i41e 3411-1-tI M -5 n 1..514 3188140.1 NOOS OES 4' 4af4n1.45 umn NOW NftIW4gW 31,93, 405W1.µ 4 . 21551565E 241r.m 0IAt 19EB 63 41.161 24172).. 40@ YOnO yE Mf' 4.It9.W 4.11255 P 1176 2µp71515 YOEII M1t1 { aff 1692011 -MI- 3 IJ z 1 N s 4-14 165- -1127 x3 081456.99 1µ1O6)9 4tt15 M 7 r -3.73 YOm) _ 1 .16M 6]511.79 29?)0.9e 2 Yale Np09 -11114 16139.24 .u 010X47 NaEw MM21 N 519.16 4.450.. 2µm41.95 11 1 249.9476 .OCO 191E1J -7 19514.}! 1611 0 34509.,10 24 1. .U5 0E15 NWIrift M44' . 46191.0 . 2430.1-3 Ya27 411..0 1 -C2, N-'111 W.71, w51µ51 246010 x 7' 1.5}90.1 2µ111w 013 uF9J0 4.141 165)0111 1 2 7,µ 21101419 I X01 2wYE0g3 11..11 411213,01I 2 .M Na. Z Z N' . -7.0 208. YOE. Nt ID w6 1µ.01 24597610E VOFa i' w6effire 31691742 145µp111 MM7 MOE31 -11 419..1 3011.)11 YaJO YOWL x31 1111.91 1600876 41111,11 n 4 YJEw N14?14W 18115, 4016151 1,14 0E0 Yaa N III S". 11014.1 1.762.1 1 .1 249085 l Y 1664442 21E1W. YOEM 4om1,18 2µ9u. Yn0 NW µ6P1495 w 16112. 0E. 0E0 0150 ' .6-76 16B.8µ 0 g 59151 Nd 1 14' 4014. 14276.9 Aam W' w 40661.. 15E54 WO' 40199x1 2 x195 1116 816511 0Ex '.• 1.42n.µ µ811a 216111450 3.114 wE1 1p14µ12 1190 It 18 70 1 2 2.114. 0Ea 11141.911 21591}4.16 91421 -112 'N' 71' 4.1].49 1607631 2µ1Po.19 x0591425 IOE43 X3r51' 1.141.2 . w Ypa4 xl 21158. Ya1 Y i' "71 24 7 - YOFA6 m-] N S1 N N W 442 - 4..7 59 141141.0 2µ9S115 LNE"WeTLANOB F AG TABLE FLAG NO. BEARING LENGTH NORTHING LASTING -1 x011 4x.441 3076.,74. x082 16118. z+eous.a M 04 Hal N-'25N -s 14 4.31 161541 2 I 1..02 7 mm -11. .11 10 2.- .. 245045114 "ON NOn 169 .60 20016148 V Q11 m,0 20761.11 Y NG1a M7WIrW 169119,13 276µp.1 Yan 4811.3 .tl 2 1681126 21164160 MY915 I wµ6061 241.5.58 Y.I4 Mam I 10y oo -0.30 x460.0.. 2 11.18 761m.0 .µ .9 Y.n 1010.11 1µ0N1.11 M[91e 'Y 1421103 2 215 003 16µm 116761. M13 161114 1691090 2.02160 216117.& r•w 42.2e M1 2 .M4 t pyy 27,12- 44)x1.19 145µ10d1 .Do" u.S N5,4?TMFW 6e' 161..3 0 1761.88 2 10.50 u ] Y 1 1 m YOB. N ..' 16 16114 R4PoIJA3 2161 n.9.,• 17 40µ1n 241 mnm MO531 1 691' f0µ 3 27611.10 Y.J1 uau 14.85' w1µ. lams 20.995 -22 000 i 4111,12 14801140 0936 -11- 0150 1 1011 Di.m 146761411 NO SCALE 41.1 A M CLM 243 NORM FRONT STREET NBWNGTEN, NORM CAROUNA 28401 TELL (916 313-IV 2 2 nHp://%wn-ko-W c3Sro LIE J WE7utm8 (CONirU®) FLAG TAB E FUG N0. BEARING LENGTH NORTHING LASTING nd ).- N90m 1 9.50 865 i 1' -. -!4s? 24m160µ 140 m 51611121 9 -.1, 4421 . ?Z. P.11n.µ 61' Jim 31,02' 4.36952 2µ18p222 J11 3)?'? • 401437 2µ1621.a m 1. 40031.17 a92ffi12 2418190 2461&0.. .nn 48i8936 201644.34 AN 16016891 162114,16 24112% 2011242 76 4.1110 201 S.a 076 16420.. 2010..15 4175 1 U.77' 16..5.8. 4)114.2) 201x241 xb ma.- .7o M 4210.3] 40µ1n 201014.16 2461907.76 . J m 414 2 462007.51, J11 1154-401't 109116.1 4.2431 2M=7.71 2µ1470.91 A84 51 .9-11 16931.. 420 20x155.1 5 60340 10213922 JIB1 I N_-1 n 164371. 1µ2I 19 Rm nm 47631415 wmrax 2461.131 5181818 Jlµ 1611).. 4.&421 2M1ean 20111114 J19x ,141 1611326 4.214 18 2014 0+.81 1162142.3 )194 JI1 .. 16931.4] 4 5.16 24eme.u 21613.21 140 ' 1 : 111. .a .0.1 ) 1 . 1 1 169213.4 9011D1 14 24k-x 4106 E01462a Jla 01131191 41461 300 NISIVIMIE 71 1a1065 1 .µ 102611.57 J1m R1,1 4 433 476101 1.9631,53 POSN,a 1276 4.165. 2.x11.81 J21 1695161 2 , .11 J1a 30] Xn' 4.x428 1.51414 .. .16x 40 93 204-&1 3. m•r 1681122 ' 2451414.. JIO IN 4 40180,1 161x,14 20210.20 31631)85 311 w 40 µ12a 2046823 112 J13 1 no- Rzor r 3 41%I.µ 1.22 5487617. 14 wOH,S 57111.1 316 z 1432 4216 4217 N Y 4.89.53 4.&451 201.1. ' 2 83 Jne ' ?N 9A JOAX +a41,a 4 62.00 xMEwd! )210 3S n 40141.00 7641.72 x63186 x026"14 J91 409.0,56 2 312 101)10.0 104614.1 a24 323 . I' -s 4o9n11 2 i 11111 335 n. +.27438 216281.13 J1ID x 1120.0 20108.64 a. 376 " 4.0561 9 105,15 14620614 S",www 41S2 1.281.14 ? zlmnzn 0 214 Jan 1 41 Eµ390.- 3 )231 St r 09-461 16917.4 2412x.14 40106,1) 16991x+ 1M11- 30 31 n 579-0.9' 169171.42 101.61) R 1431 4a171a MW 1-µ2p31.. 3a 31 16311.1 4..418 1.200131 1453163 316 16761413 2-M1 )241 So.w 161637. 30111µ91 -2 S14'-WWW µ 2.1501- IL J9u -`f W 20, 4.1151 101 1e J- ?01 µ.µ0 1µ1m].62 aw . Je )247 1 2461ma12 1 341 J1µ W M A I . ? -,1 013919 .1 2 261 "1.n 20111. WETLANDS DELINEATION SURVEY FOR 9.e sEnt 4F s WEYERHAEUSER REAL ESTATE 113. F DEVELOPMENT COMPANY PORTION OF ONSLOW 19 TRACT ?L RNCHL4NAS TOWNmHr - 00&1411 - NORTH CAROLINA i., 19.64 1x146 29, 2007 NO Sous PROJECT M : 009100163 PROJ. SV117 CLJ DRAWN BY : ACS FIELD BN : W1013/56 - W COMP, FILE ; 94101-009100183-R SHEET 0 : SHEET 5 OF 14 DWG. y: LAE J w1E1LAND8 L14F ? MOD 11E11+1N,1B FUG TABLE FLAG 570, BEAPoNG LENG11 NGRIMINC EASING Yoos E,ay' 4punsr :16.151 MOO4 PE n x421. S-III2'3 11521.2 1µV96572 wsa4ol 541111 P OE 10 031 N59m,Qc`w I .IV 10&11&% 1 9.16 LPE wo wen Ame LIE H WETLANDS FLAG TABLE FUG NO. BEARING LENGTH NORTHING FASTING [ Rw1 R ro 643 IRf 'x 050' v 46857," 108589.2 1464193.. 101118.18 x3 Hi 9-21' 1 11 46}741= 24641015 1461177.8 Xs I'4' 410' .e7M9/ 2010"61 x s 'ssl aae* an .es x] HB sn34X'9 4T ' 4s33* 18 46rMr 41 0116= :460285 14 x01851 H9 5 H x.'452 'W & . . X10 4474879 111,.117 468 1 24B3Bn.11 N13 2 r5 218R52d0 2 141Ta937 H15 -V5 I' r m 6.13 311= 3.13 2"MM74 61 OY 1-2.04 3/608]0. 1 . 11025'27 A]' 2bRd0.m .85X1] x0161=1 .e1-18 203511,54 ,SOYM'r` S02'arl 0701 14 Sw 203 .m 2 35r . II-21 2191 H32 51 1 "9.77 1031600 HM -WVa 1690' t] .1]61.95 .17132 2 m -- H36 .sr 0704.m 2034-.= HI a3" 0'00.0 .r"1." 246 2183136." Mm .4' 085285 383"185 X19 alt ' -SKM 246 47 X. -TITE al" 0]51610 115"2233 W3 b1011J .1050 N7W2M 2033X8 NN INS 477856. 013-85 105116" 2b"4M16 2.=15.. X11 IM2M97 14"22. X0 07855)1 M181 2 xw 0778,77 "M 2X8577 WI 077-.2 07 2b31Mm 1011X0 X52 35 -6 401026 60 1154 469"w 061149.71 10361" 2030711 1155 .6912. 2 x85 X57 W 212p'_ b5L' 0853485 wr.A1 24611850] 21"0111 x85 .61077 146311.11 x39 0 4677x- 106881,17 . 146130=.85 10 4 1161 08641.. II483w10 x" .885285 10"800 x" .?$}T_ 105362. 1463Rd. 854 Y --.7:_ ."ma 20"8578 N" x% 1-4 0549885 0307.1 24B1w42J 21"2al,m 116] N-213% n7v 1601.0 15 NO N" 1641339 0819685 103281,77 20.11 Hm 1 42 Ia X11 HIS 'IV 4819.16 10". , ' 11631-n INN 0859-S ' X73 .663 1 A . 401610.]1 IS 10061,44 H]4 Hn 174577.41 20.m.fi] Hm 408522" 14639..61 H77 . 4 20X247 XM T 185eu61111 4 2b]Ji1.14 xIm 01 1J H. x85 _ 116191.85 14"0185 H" x84 M-7 85 85 2. 16. 8 2031 ,m " H- 0 9 2mX0 2 v M-2 1 10]01 r x 85 . a zb3 4 0601.19 I4 x03]6 1685 H. www.6 w 2 119111= Oitll 46991 38 5 24"4026 ALC OTCII ALM-IG 0111 E7-69 0 .32 1050 .M =031},87 AL-w 0101 -.1.1.25 E41 0'1, AL.G afal MIN .72310 10JSn.- ALaG aT-I AIWG OHW .776 1 0110. Sr 11068077 20JSM. AL-C OGOI f 1' 01 7 -1960 ONM =3 01d"11 0aam-l 3.11 u6C olrzx 1 1b a1 llgm dn4 . nX NI-Q-11-10 4Jkw 4 24 A pTCX 2.X1416 24".101 ull 71,0110 0101 'd' Y g 2.72.18 IP:N ALONG DTM M?IWZITE 24W5711 2035 163 b13 -11 21611260 g=al 20a5a,m DITCH AL "W4n2-4 1' 4-85114 0- 10 2" AL6C gICN manml 22 4037.19 71-10 0101 48569.11 10110,15 .520110 piCN w311J1 m3Wl%JIl AIAiC piAl i 0854'3.21 2 71 Acow aTCN ALMS -ICX --Hummx- -1 48591110 712 9852 5 MORN AIAIO 01.01 185 16 ALMG (X- N"75,16% j- 185X4.85 340W". ALa10 mW ZZ M- 485X0,14 20178501 u0N0 aiW It 20-UII! uqn ALONG 1-.785 ImSm.- 1b3700.w i ITCH ALON 10377.25 .47110 GITCN lm ulxla -1- w 71 -4DITm 0005904 1453611.0 N-w 0=1.11 ]LG10 T-i 12 40796" A 11,1 2076. M01w T. 46TI.SJ = ALONG NTM Dl- 01}14,08 16]11,11 2008527 204985,2 alp 41018 .8851.85 z04121JG AL.- -T-1 46"7.91 94M56AI nE W R M-G R 40mMm 0716. 20IN L. .. 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REAL ESTATE WEYERHAEUSER IN N 'Im 500 113 NORTH FRONT STREET WILM ' NORTH CARpNA 7B401 iV T DEVELOPMENT COMPANY PORTION OF ONSLOW 19 TRACT IEIE (910 "' M6 FAX: ((910 R51-87az hltp://,m.Mlmvwdwm E (. , MCMANW TOWMMP - OMOW - NOME CAROLINA nine EB, 2007 SLAGS 1' =200' PROJECT N OD9100163 PROD. SWR DLJ DRAWN BY :ACS FIELD BK.: W1013/56 - LJ COMP. RILE : _131-33910I63-R SHEET N :SHEET 7 OF 14 DWO. # : ?j r ( C7 f so * ?? WETLANDS DELINEATION SURVEY FOR PROJECT y : 009100163 PROI S'NR : ow : DRAWN BY Acs SCALE: 1•.2? """"""" o H 2 ? ? p WEYERHAEUSER REAL ESTATE FIELD B 013/58 - U -?-N 217 NORTH FRONT STREET SEAL ` a DEVELOPMENT COMPANY L t roua . FlE 101-ooslomsa? rr R u 0 ew W"INCTp, NORTH CAROLINA 2&0 WE 9107 ]IS-1W8 L9B S? PORTION OF ONSLOW 19 TRACT SHEET E : SHEET 6 OF 14 hNp: FAX:: (910) 251-0262 //rnnmxWnaee0.xn 1. RICNANDS TOIFNSHID - ONSLOA' - NORTH CAROLINA ' DATE Ime 89, 2007 SCAIS: Y a 800 D%0. d? 8 re- PROJECT / : 009100185 PROJ. SVYR : DW DRAWN BY ;ACS FIELD BK NT013/58 - LJ COMP. FILE : vx101-009100163 A OF 14 SHEET / : SHEET 901F11463 OWO. # ?? WETLANDS DELINEATION SURVEY FOR g°` a WEYERHAEUSER REAL ESTATE 243 NORTH FROM STREET Lin DEVELOPMENT COMPANY I?T?bd_,ft w?uwiNCrai• NORTH cxiwNA za+m 4y ?' PORTION OF ONSLOW 19 TRACT FA910? 343-104a X f 910 751-8267 E. .^" RICHWNAW TOWNSHIP - ONSWIV - NOR777 CAROWNA Mtp; //www.mdimamd.con .n.,4 Jmw BB, 5007 SCAM 1, =200' Lamm s m? \\ 44 \ a nuu u°a \ ^un 0uae !? V rx ?"+ \ Y+ ?.uw \ M' \ ...?Ir?. :..vana \ \ 'rtN. ? ? cua ?( ?pLL 11 '?u .„•! = e WETLANDS DELINEATION SURVEY FOR WEYERHAEUSER REAL ESTATE PROJECT y:DDSlootea PROJOs. SV sure aJ DRAWN By Acs SCALE. r zoo' " 243 NOIM FRONT STREET '1" CARDUNA 2MI NORT v a seA? " t d Ldpr° 4 DEVELOPMENT COMPANY P 2e X01 /55BOSia J SHEET eer to c tc s MLMNM, H ESBw)) S }IWB b, $1 PORTION OF ONSLOW 19 TRACT n r FAIL (BIC)131-A2E1 JOKE RICIRANA4 TOIWNSL? - ONSLOI - NOM CAROLING enp://m maN cratl.am ? 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NORTH AA00NA 26401 -- 910 343-ION FAX 910 251-8582 http'??w4M.mvdmua6,arn WETLANDS DELINENATION SURVEY sPa WEYERHAEUSER REAL ESTATE DEVELOPMENT COMPANY Lae PORTION OF ONSLOW 19 TRACT RICNUNOS TOWNa7NP - ONSLOIF - NORTH CAROLINA -- W June 28, 2007 SCALE: 1' = 200• PROJECT Y : 0091001- PRO7, sWR : 0LJ CRAwN BY : ACS HELD BK. M013/16 - U COMP, RLE v 101-009100163 F SHEET # : SHEET 11 OF 14 Dwc. A '. WE MIS H2O FT.. 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TRACT 1 \ 44? ru`?"Fpt ?' vRes rom B ? ?i h5 + aV . '.IQ i, "nJ P595 j e ? \ \, i n': a y'°? xt.x? ?? 9SHyt? t _ °v lna i ? BBY1 OE'E ? ,I{PO \ ? - J+R'1'f +}A.+.P !Oti ?? . + 0 ? ,;J07 FG ? SCALE: 1' - 200' o so u A 11"W&CREM 243 NORTH FRONT SVEET NIU9NGTCN, NORTH CAROUNA 28401 1ELE 910) 3{3-10iB FA# 970} 251-8287 AGp:/j;". ckiT-d- WETLANDS DELINEATION SURVEY FUR sFAL i REAL ESTATE WEYERHAEUSER ?e DEVELOPMENT COMPANY PORTION OF ONSLOW 19 TRACT J2ramum3 TOIINSIl6 - ONSWW - NORTH CAROLINA fuse 29.2007 Sum 1"- 200, PROJECT IF ', 009100165 PROs. SVYR Du DRAWN BY', ACS FlELD BK. W1013/56 - LJ COMP. FILE : -101-009100163_R SHEET 1: SHEET 13 OF 1+ DWG. J 1-,--i ulow a U 'im rorx a 2 '+?gvralm' eW R'n? ?TWF S' (¶E RIM 10 OJwER) im - M v WETLANDS DELIT1ON SURYEY PROJECT q 009100163 PROJ. svB . SCALE r . sao 0 M ?-?-+ 243 NORTH FRONT s?6n V'Vw?L •' eta m WILMINGTON, TELL (9100? xslaa fA%: (910) 281-8'[82 eu9:/M*. %v lraa ^ SEAL w cn g0 t DATE 09 WEYEKIEGWER REAL ESTATE DE aOFMENT COMYAJI PORTION OF ON&LOW 19 TRACT 4T RAMAW 4YlhN9? - ON.4LOE -NORM C LIxA rm, ae a667 scArs r = AC DRAWN By : us nFJn BK. : vnola/ss - w ,FIELD Flw: 101 -'009100163R 6x6¢? p :SHE a or u WG'. ?: APPENDIX C. SITE PHOTOGRAPHS 1) View of channelized section of HU-2 Batchelors Delight Mitigation Bank Restoration Plan 01-09-168 LMG LAND IIIANAGENIEN-1 GROUP-, f+?vi?cunn a?rt?l Corisullc?nts Site Photographs 2) View of cultivated fields adjacent to boundary ditch 3) View of existing conditions at HU-1 4) View existing valley in the headwaters of HU-1 Batchelors Delight Mitigation Bank Restoration Plan 01-09-168 LMG LAND IIIANAGENIEN-1 GROUP-, f+?vi?cunn a?rt?l Corisullc?nts Site Photographs 5) View of floodplain adjacent to HU-1 Batchelors Delight Mitigation Bank Restoration Plan 01-09-168 LMG Ln:V 11 nlel\nC;lA1L'q7 GROUP-, . f+?vr.cunnerrtol Coresultams Site Photographs 6) View of HE-4 Preservation 7) View of Impounded area of HU-2 (north of Maready Rd.) 8) View of ponded channel in BD-4 (north of Maready Rd.) Batchelors Delight Mitigation Bank Restoration Plan 01-09-168 LMG LAND 111ANAGENIEN-1 GROUP-, f+?vi?cunn a?rt?l Corisultc?nts Site Photographs APPENDIX D. USACE STREAM ASSESSMENT DATA FORMS Bachelors Delight Stream and Wetland Mitigation Bank 0 1,200 2,400 3,600 Onslow County Feet LMG LANll MANAGEMhN'1' GUOUP nc Env--ntul Consultants USACE AID# Provide the following information for the stream reach under assessment. Hewl Applicant's name: WREDCO attn: Sandy McLendon 3. Date of evaluation: 1/8/09 5. Name of stream: Hewitts Branch 7. Approximate drainage area: +/- 200 acres 9. Length of reach evaluated: 200 feet 4. Time of evaluation: 10:45 6. River basin: New River 8. Stream order: first 10. County: Onslow 11. Site coordinates (if known): prefer in decimal degrees. 12. Subdivision name (if any): n/a Latitude (ex. 34.872312): 34.8640 Longitude (ex. -77.556611): 77.4668 Method location determined (circle): GPS Topo Sheet Ortho (Aerial) Photo/GI Other GIS Other 13. Location of reach under evaluation (note nearby roads an an mar ?s and attach map identifying stream(s) location): (see GIS map showing data points) 14. Proposed channel work (if any):proposed channel restoration 15. Recent weather conditions: mild, 16. Site conditions at time of visit: warm, sunny 17. Identify any special waterway classifications known: Section 10 Tidal Waters Essential Fisheries Habitat Trout Waters Outstanding Resource Waters Nutrient Sensitive Waters Water Supply Watershed (I-IV) 18. Is there a pond or lake located upstream of the evaluation point? YE NO yes, estimate the water surface area: 19. Does channel appear on USGS quad map? YES O 20. Does channel appear on USDA Soil Survey? YE NO 21. Estimated watershed land use: 0 % Residential 0 % Commercial 0 % Industrial 0 % Agricultural 50 % Forested 50 % Cleared / Logged D-% Other ( ) 22. Bankfull width: 8 feet 23. Bank height (from bed to top of bank): 3 feet 24. Channel slope down center of stream: X Flat (0 to 2%) Gentle (2 to 4%) Moderate (4 to 10%) Steep (>10%) 25. Channel sinuosity: X Straight Occasional bends Frequent meander Very sinuous Braided channel Instructions for completion of worksheet (located on page 2): Begin by determining the most appropriate ecoregion based on location, terrain, vegetation, stream classification, etc. Every characteristic must be scored using the same ecoregion. Assign points to each characteristic within the range shown for the ecoregion. Page 3 provides a brief description of how to review the characteristics identified in the worksheet. Scores should reflect an overall assessment of the stream reach under evaluation. If a characteristic cannot be evaluated due to site or weather conditions, enter 0 in the scoring box and provide an explanation in the comment section. Where there are obvious changes in the character of a stream under review (e.g., the stream flows from a pasture into a forest), the stream may be divided into smaller reaches that display more continuity, and a separate form used to evaluate each reach The total score assigned to a stream reach must range between 0 and 100, with a score of 100 representing a stream of the highest quality. Total Score (from reverse): 32 Comments: Form was completed under drought conditions. Although the low score accurately reflects the fact that it is a man-made ditch. it is likelv to have water in the channel and/or flow durina the winter Evaluator's Signature Date 1/8/09 This channel evaluation form is intended to be used only as a guide to assist landowners and environmental professionals in gathering the data required by the United States Army Corps of Engineers to make a preliminary assessment of stream quality. The total score resulting from the completion of this form is subject to USACE approval and does not imply a particular mitigation ratio or requirement. Form subject to change - version 06/03. To Comment, please call 919-876-8441 x 26. DWQ# Site # (indicate on attached map) FE11 STREAM QUALITY ASSESSMENT WORKSHEET -AQP 2. Evaluator's name: Corev Novak STREAM QUALITY ASSESSMENT WORKSHEET # ECOREGION POINT RANGE CHARACTERISTICS SCORE Coastal Piedmont Mountain 1 Presence of flow / persistent pools in stream 0-5 0-4 0-5 2 (no flow or saturation = 0; strong flow = max points) 2 Evidence of past human alteration 0-6 0-5 0-5 1 (extensive alteration = 0; no alteration = max points) 3 Riparian zone 0-6 0-4 0-5 2 (no buffer = 0; contiguous, wide buffer = max points) 4 Evidence of nutrient or chemical discharges 0-5 0-4 0-4 5 (extensive discharges = 0; no discharges = max points) a 5 Groundwater discharge 0-3 0-4 0-4 1 U (no discharge = 0; springs, seeps, wetlands, etc. = max points) 6 Presence of adjacent floodplaln 0-4 0-4 0-2 2 (no floodplain = 0; extensive floodplain = max points) 7 Entrenchment / floodplain access 0-5 0-4 0-2 0 (deeply entrenched = 0; frequent flooding = max points) 8 Presence of adjacent wetlands 0-6 0-4 0-2 2 (no wetlands = 0; large adjacent wetlands = max points) 9 Channel sinuosity 0-5 0-4 0-3 (extensive channelization = 0; natural meander = max points) 10 Sediment input 0-5 0-4 0-4 2 (extensive deposition= 0; little or no sediment = max points) 11 Size & diversity of channel bed substrate NA* 0-4 0-5 N/A (fine, homogenous = 0; large, diverse sizes = max points) 12 Evidence of channel incision or widening 0-5 0-4 0-5 (deeply incised = 0; stable bed & banks = max points) 0 F'. 13 Presence of major bank failures 0-5 0-5 0-5 3 a (severe erosion = 0; no erosion, stable banks = max points) 14 Root depth and density on banks 0-3 0-4 0-5 1 H (no visible roots = 0; dense roots throughout = max points) 15 Impact by agriculture, livestock, or timber production 0-5 0-4 0-5 2 (substantial impact =0; no evidence = max points) 16 Presence of riffle-pool/ripple-pool complexes 0-3 0-5 0-6 0 (no riffles/ripples or pools = 0; well-developed = max points) 17 Habitat complexity 0-6 0-6 0-6 1 (little or no habitat = 0; frequent, varied habitats = max points) 18 Canopy coverage over streambed 0-5 0-5 0-5 3 (no shading vegetation = 0; continuous canopy = max points) 19 Substrate embeddedness NA* 0-4 0-4 N/A (deeply embedded = 0; loose structure = max) 20 Presence of stream invertebrates (see page 4) 0-4 0-5 0-5 1 (no evidence = 0; common, numerous types = max points) 21 Presence of amphibians 0-4 0-4 0-4 1 O (no evidence = 0; common, numerous types = max points) C 22 Presence of fish 0-4 0-4 0-4 0 (no evidence = 0; common, numerous types = max points) 23 Evidence of wildlife use 0-6 0-5 0-5 3 (no evidence = 0; abundant evidence = max points) Total Points Possible 100 100 100 TOTAL SCORE (also enter on first page) 32 * These characteristics are not assessed in coastal streams. USACE AID# Provide the following information for the stream reach under assessment. Hew2 Applicant's name: WREDCO attn: Sandy McLendon 3. Date of evaluation: 1/8/09 5. Name of stream: Hewitts Branch 7. Approximate drainage area: +/- 200 acres 9. Length of reach evaluated: 200 feet 4. Time of evaluation: 12:30 6. River basin: New River 8. Stream order: first 10. County: Onslow 11. Site coordinates (if known): prefer in decimal degrees. 12. Subdivision name (if any): n/a Latitude (ex. 34.872312): 34.8627 Longitude (ex. -77.556611): 77.4630 Method location determined (circle): GPS Topo Sheet Ortho (Aerial) Photo/GI Other GIS Other 13. Location of reach under evaluation (note nearby roads an an mar ?s and attach map identifying stream(s) location): (see GIS map showing data points) 14. Proposed channel work (if any):proposed channel restoration 15. Recent weather conditions: mild 16. Site conditions at time of visit: warm, sunny 17. Identify any special waterway classifications known: Section 10 Tidal Waters Essential Fisheries Habitat Trout Waters Outstanding Resource Waters Nutrient Sensitive Waters Water Supply Watershed (I-IV) 18. Is there a pond or lake located upstream of the evaluation point? YE NO yes, estimate the water surface area: 19. Does channel appear on USGS quad map? YES O 20. Does channel appear on USDA Soil Survey? YE NO 21. Estimated watershed land use: 0 % Residential 0 % Commercial 0 % Industrial 0 % Agricultural 50 % Forested 50 % Cleared / Logged D-% Other ( ) 22. Bankfull width: 7 feet 23. Bank height (from bed to top of bank): 2.5 feet 24. Channel slope down center of stream: X Flat (0 to 2%) Gentle (2 to 4%) Moderate (4 to 10%) Steep (>10%) 25. Channel sinuosity: X Straight Occasional bends Frequent meander Very sinuous Braided channel Instructions for completion of worksheet (located on page 2): Begin by determining the most appropriate ecoregion based on location, terrain, vegetation, stream classification, etc. Every characteristic must be scored using the same ecoregion. Assign points to each characteristic within the range shown for the ecoregion. Page 3 provides a brief description of how to review the characteristics identified in the worksheet. Scores should reflect an overall assessment of the stream reach under evaluation. If a characteristic cannot be evaluated due to site or weather conditions, enter 0 in the scoring box and provide an explanation in the comment section. Where there are obvious changes in the character of a stream under review (e.g., the stream flows from a pasture into a forest), the stream may be divided into smaller reaches that display more continuity, and a separate form used to evaluate each reach The total score assigned to a stream reach must range between 0 and 100, with a score of 100 representing a stream of the highest quality. Total Score (from reverse): 37 Comments: Form was completed under drought conditions. Although the low score accurately reflects the fact that it is a man-made ditch. it is likelv to have water in the channel and/or flow durina the winter Evaluator's Signature Date 1/8/09 This channel evaluation form is intended to be used only as a guide to assist landowners and environmental professionals in gathering the data required by the United States Army Corps of Engineers to make a preliminary assessment of stream quality. The total score resulting from the completion of this form is subject to USACE approval and does not imply a particular mitigation ratio or requirement. Form subject to change - version 06/03. To Comment, please call 919-876-8441 x 26. DWQ# Site # (indicate on attached map) FE11 STREAM QUALITY ASSESSMENT WORKSHEET -AOQV 2. Evaluator's name: Corev Novak STREAM QUALITY ASSESSMENT WORKSHEET # ECOREGION POINT RANGE CHARACTERISTICS SCORE Coastal Piedmont Mountain 1 Presence of flow / persistent pools in stream 0-5 0-4 0-5 3 (no flow or saturation = 0; strong flow = max points) 2 Evidence of past human alteration 0-6 0-5 0-5 1 (extensive alteration = 0; no alteration = max points) 3 Riparian zone 0-6 0-4 0-5 1 (no buffer = 0; contiguous, wide buffer = max points) 4 Evidence of nutrient or chemical discharges 0-5 0-4 0-4 4 (extensive discharges = 0; no discharges = max points) a 5 Groundwater discharge 0-3 0-4 0-4 2 U (no discharge = 0; springs, seeps, wetlands, etc. = max points) 6 Presence of adjacent floodplaln 0-4 0-4 0-2 2 (no floodplain = 0; extensive floodplain = max points) 7 Entrenchment / floodplain access 0-5 0-4 0-2 0 (deeply entrenched = 0; frequent flooding = max points) 8 Presence of adjacent wetlands 0-6 0-4 0-2 3 (no wetlands = 0; large adjacent wetlands = max points) 9 Channel sinuosity 0-5 0-4 0-3 2 (extensive channelization = 0; natural meander = max points) 10 Sediment input 0-5 0-4 0-4 3 (extensive deposition= 0; little or no sediment = max points) 11 Size & diversity of channel bed substrate NA* 0-4 0-5 N/A (fine, homogenous = 0; large, diverse sizes = max points) 12 Evidence of channel incision or widening 0-5 0-4 0-5 (deeply incised = 0; stable bed & banks = max points) 0 F'. 13 Presence of major bank failures 0-5 0-5 0-5 3 a (severe erosion = 0; no erosion, stable banks = max points) 14 Root depth and density on banks 0-3 0-4 0-5 2 H (no visible roots = 0; dense roots throughout = max points) 15 Impact by agriculture, livestock, or timber production 0-5 0-4 0-5 1 (substantial impact =0; no evidence = max points) 16 Presence of riffle-pool/ripple-pool complexes 0-3 0-5 0-6 0 (no riffles/ripples or pools = 0; well-developed = max points) 17 Habitat complexity 0-6 0-6 0-6 2 (little or no habitat = 0; frequent, varied habitats = max points) 18 Canopy coverage over streambed 0-5 0-5 0-5 2 (no shading vegetation = 0; continuous canopy = max points) 19 Substrate embeddedness NA* 0-4 0-4 N/A (deeply embedded = 0; loose structure = max) 20 Presence of stream invertebrates (see page 4) 0-4 0-5 0-5 1 (no evidence = 0; common, numerous types = max points) 21 Presence of amphibians 0-4 0-4 0-4 1 O (no evidence = 0; common, numerous types = max points) C 22 Presence of fish 0-4 0-4 0-4 0 (no evidence = 0; common, numerous types = max points) 23 Evidence of wildlife use 0-6 0-5 0-5 4 (no evidence = 0; abundant evidence = max points) Total Points Possible 100 100 100 TOTAL SCORE (also enter on first page) 37 * These characteristics are not assessed in coastal streams. USACE AID# Provide the following information for the stream reach under assessment. Hew3 Applicant's name: WREDCO attn: Sandy McLendon 3. Date of evaluation: 1/8/09 5. Name of stream: Hewitts Branch 7. Approximate drainage area: +/_ 200 acres 9. Length of reach evaluated: 200 feet 2. Evaluator's name: Corev Novak 4. Time of evaluation: 13: 00 6. River basin: New River 8. Stream order: first 10. County: Onslow 11. Site coordinates (if known): prefer in decimal degrees. 12. Subdivision name (if any): n/a Latitude (ex. 34.872312): 34.8648 Longitude (ex. -77.556611): 77.4604 Method location determined (circle): GPS Topo Sheet Ortho (Aerial) Photo/GI Other GIS Other 13. Location of reach under evaluation (note nearby roads an an mar ?s and attach map identifying stream(s) location): (see GIS map showing data points) 14. Proposed channel work (if any): proposed channel preservation 15. Recent weather conditions: mild 16. Site conditions at time of visit: warm, sunny 17. Identify any special waterway classifications known: Section 10 Tidal Waters Essential Fisheries Habitat Trout Waters Outstanding Resource Waters Nutrient Sensitive Waters Water Supply Watershed (I-IV) 18. Is there a pond or lake located upstream of the evaluation point? YE NO yes, estimate the water surface area: 19. Does channel appear on USGS quad map? YES O 20. Does channel appear on USDA Soil Smvey? YES O 21. Estimated watershed land use: 0 % Residential 50 % Forested 22. Bankfull width: 4 feet 0 % Commercial 0 % Industrial 0 % Agricultural 50 % Cleared / Logged D-% Other ( ) 23. Bank height (from bed to top of bank): 2 feet 24. Channel slope down center of stream: X Flat (0 to 2%) Gentle (2 to 41/o) Moderate (4 to 10%) Steep (>10%) 25. Channel sinuosity: Straight Occasional bends Frequent meander Very sinuous X Braided channel Instructions for completion of worksheet (located on page 2): Begin by determining the most appropriate ecoregion based on location, terrain, vegetation, stream classification, etc. Every characteristic must be scored using the same ecoregion. Assign points to each characteristic within the range shown for the ecoregion. Page 3 provides a brief description of how to review the characteristics identified in the worksheet. Scores should reflect an overall assessment of the stream reach under evaluation. If a characteristic cannot be evaluated due to site or weather conditions, enter 0 in the scoring box and provide an explanation in the comment section. Where there are obvious changes in the character of a stream under review (e.g., the stream flows from a pasture into a forest), the stream may be divided into smaller reaches that display more continuity, and a separate form used to evaluate each reach The total score assigned to a stream reach must range between 0 and 100, with a score of 100 representing a stream of the highest quality. Total Score (from reverse): 73 Comments: proposed area for stream preservation Evaluator's Signature Date 1/8/09 This channel evaluation form is intended to be used only as a guide to assist landowners and environmental professionals in gathering the data required by the United States Army Corps of Engineers to make a preliminary assessment of stream quality. The total score resulting from the completion of this form is subject to USACE approval and does not imply a particular mitigation ratio or requirement. Form subject to change - version 06/03. To Comment, please call 919-876-8441 x 26. DWQ# Site # (indicate on attached map) FE11 STREAM QUALITY ASSESSMENT WORKSHEET -AOQV STREAM QUALITY ASSESSMENT WORKSHEET # ECOREGION POINT RANGE CHARACTERISTICS SCORE Coastal Piedmont Mountain 1 Presence of flow / persistent pools in stream 0-5 0-4 0-5 5 (no flow or saturation = 0; strong flow = max points) 2 Evidence of past human alteration 0-6 0-5 0-5 4 (extensive alteration = 0; no alteration = max points) 3 Riparian zone 0-6 0-4 0-5 3 (no buffer = 0; contiguous, wide buffer = max points) 4 Evidence of nutrient or chemical discharges 0-5 0-4 0-4 5 (extensive discharges = 0; no discharges = max points) a 5 Groundwater discharge 0-3 0-4 0-4 3 U (no discharge = 0; springs, seeps, wetlands, etc. = max points) 6 Presence of adjacent floodplaln 0-4 0-4 0-2 3 (no floodplain = 0; extensive floodplain = max points) 7 Entrenchment / floodplain access 0-5 0-4 0-2 5 (deeply entrenched = 0; frequent flooding = max points) 8 Presence of adjacent wetlands 0-6 0-4 0-2 4 (no wetlands = 0; large adjacent wetlands = max points) 9 Channel sinuosity 0-5 0-4 0-3 5 (extensive channelization = 0; natural meander = max points) 10 Sediment input 0-5 0-4 0-4 5 (extensive deposition= 0; little or no sediment = max points) 11 Size & diversity of channel bed substrate NA* 0-4 0-5 N/A (fine, homogenous = 0; large, diverse sizes = max points) 12 Evidence of channel incision or widening 0-5 0-4 0-5 (deeply incised = 0; stable bed & banks = max points) 5 F'. 13 Presence of major bank failures 0-5 0-5 0-5 4 a (severe erosion = 0; no erosion, stable banks = max points) 14 Root depth and density on banks 0-3 0-4 0-5 2 H (no visible roots = 0; dense roots throughout = max points) 15 Impact by agriculture, livestock, or timber production 0-5 0-4 0-5 3 (substantial impact =0; no evidence = max points) 16 Presence of riffle-pool/ripple-pool complexes 0-3 0-5 0-6 1 (no riffles/ripples or pools = 0; well-developed = max points) 17 Habitat complexity 0-6 0-6 0-6 5 (little or no habitat = 0; frequent, varied habitats = max points) 18 Canopy coverage over streambed 0-5 0-5 0-5 3 (no shading vegetation = 0; continuous canopy = max points) 19 Substrate embeddedness NA* 0-4 0-4 N/A (deeply embedded = 0; loose structure = max) 20 Presence of stream invertebrates (see page 4) 0-4 0-5 0-5 3 (no evidence = 0; common, numerous types = max points) 21 Presence of amphibians 0-4 0-4 0-4 2 O (no evidence = 0; common, numerous types = max points) C 22 Presence of fish 0-4 0-4 0-4 0 (no evidence = 0; common, numerous types = max points) 23 Evidence of wildlife use 0-6 0-5 0-5 3 (no evidence = 0; abundant evidence = max points) Total Points Possible 100 100 100 TOTAL SCORE (also enter on first page) 73 * These characteristics are not assessed in coastal streams. USACE AID# Provide the following information for the stream reach under assessment. Hew4 Applicant's name: WREDCO attn: Sandy McLendon 3. Date of evaluation: 1/8/09 5. Name of stream: Hewitts Branch 7. Approximate drainage area: +/_ 200 acres 9. Length of reach evaluated: 200 feet 2. Evaluator's name: Corev Novak 4. Time of evaluation: 14:20 6. River basin: New River 8. Stream order: second 10. County: Onslow 11. Site coordinates (if known): prefer in decimal degrees. 12. Subdivision name (if any): n/a Latitude (ex. 34.872312): 34.8610 Longitude (ex. -77.556611): 77.4612 Method location determined (circle): GPS Topo Sheet Ortho (Aerial) Photo/GI Other GIS Other 13. Location of reach under evaluation (note nearby roads an an mar ?s and attach map identifying stream(s) location): (see GIS map showing data points) 14. Proposed channel work (if any): proposed channel preservation 15. Recent weather conditions: mild 16. Site conditions at time of visit: warm, sunny 17. Identify any special waterway classifications known: Section 10 Tidal Waters Essential Fisheries Habitat Trout Waters Outstanding Resource Waters Nutrient Sensitive Waters Water Supply Watershed (I-IV) 18. Is there a pond or lake located upstream of the evaluation point? YE NO yes, estimate the water surface area: 19. Does channel appear on USGS quad map? YES O 20. Does channel appear on USDA Soil Smvey? YES O 21. Estimated watershed land use: 0 % Residential 50 % Forested 22. Bankfull width: 10 feet 0 % Commercial 0 % Industrial 0 % Agricultural 50 % Cleared / Logged D-% Other ( ) 23. Bank height (from bed to top of bank): 1 feet 24. Channel slope down center of stream: X Flat (0 to 2%) Gentle (2 to 41/o) Moderate (4 to 10%) Steep (>10%) 25. Channel sinuosity: Straight Occasional bends Frequent meander Very sinuous X Braided channel Instructions for completion of worksheet (located on page 2): Begin by determining the most appropriate ecoregion based on location, terrain, vegetation, stream classification, etc. Every characteristic must be scored using the same ecoregion. Assign points to each characteristic within the range shown for the ecoregion. Page 3 provides a brief description of how to review the characteristics identified in the worksheet. Scores should reflect an overall assessment of the stream reach under evaluation. If a characteristic cannot be evaluated due to site or weather conditions, enter 0 in the scoring box and provide an explanation in the comment section. Where there are obvious changes in the character of a stream under review (e.g., the stream flows from a pasture into a forest), the stream may be divided into smaller reaches that display more continuity, and a separate form used to evaluate each reach The total score assigned to a stream reach must range between 0 and 100, with a score of 100 representing a stream of the highest quality. Total Score (from reverse): 82 Comments: proposed area for stream preservation Evaluator's Signature Date 1/8/09 This channel evaluation form is intended to be used only as a guide to assist landowners and environmental professionals in gathering the data required by the United States Army Corps of Engineers to make a preliminary assessment of stream quality. The total score resulting from the completion of this form is subject to USACE approval and does not imply a particular mitigation ratio or requirement. Form subject to change - version 06/03. To Comment, please call 919-876-8441 x 26. DWQ# Site # (indicate on attached map) FE11 STREAM QUALITY ASSESSMENT WORKSHEET -AOQV STREAM QUALITY ASSESSMENT WORKSHEET # ECOREGION POINT RANGE CHARACTERISTICS SCORE Coastal Piedmont Mountain 1 Presence of flow / persistent pools in stream 0-5 0-4 0-5 5 (no flow or saturation = 0; strong flow = max points) 2 Evidence of past human alteration 0-6 0-5 0-5 4 (extensive alteration = 0; no alteration = max points) 3 Riparian zone 0-6 0-4 0-5 5 (no buffer = 0; contiguous, wide buffer = max points) 4 Evidence of nutrient or chemical discharges 0-5 0-4 0-4 5 (extensive discharges = 0; no discharges = max points) a 5 Groundwater discharge 0-3 0-4 0-4 3 U (no discharge = 0; springs, seeps, wetlands, etc. = max points) 6 Presence of adjacent floodplaln 0-4 0-4 0-2 4 (no floodplain = 0; extensive floodplain = max points) 7 Entrenchment / floodplain access 0-5 0-4 0-2 5 (deeply entrenched = 0; frequent flooding = max points) 8 Presence of adjacent wetlands 0-6 0-4 0-2 6 (no wetlands = 0; large adjacent wetlands = max points) 9 Channel sinuosity 0-5 0-4 0-3 5 (extensive channelization = 0; natural meander = max points) 10 Sediment input 0-5 0-4 0-4 5 (extensive deposition= 0; little or no sediment = max points) 11 Size & diversity of channel bed substrate NA* 0-4 0-5 N/A (fine, homogenous = 0; large, diverse sizes = max points) 12 Evidence of channel incision or widening 0-5 0-4 0-5 (deeply incised = 0; stable bed & banks = max points) 5 F'. 13 Presence of major bank failures 0-5 0-5 0-5 3 a (severe erosion = 0; no erosion, stable banks = max points) 14 Root depth and density on banks 0-3 0-4 0-5 2 H (no visible roots = 0; dense roots throughout = max points) 15 Impact by agriculture, livestock, or timber production 0-5 0-4 0-5 3 (substantial impact =0; no evidence = max points) 16 Presence of riffle-pool/ripple-pool complexes 0-3 0-5 0-6 2 (no riffles/ripples or pools = 0; well-developed = max points) 17 Habitat complexity 0-6 0-6 0-6 6 (little or no habitat = 0; frequent, varied habitats = max points) 18 Canopy coverage over streambed 0-5 0-5 0-5 4 (no shading vegetation = 0; continuous canopy = max points) 19 Substrate embeddedness NA* 0-4 0-4 N/A (deeply embedded = 0; loose structure = max) 20 Presence of stream invertebrates (see page 4) 0-4 0-5 0-5 3 (no evidence = 0; common, numerous types = max points) 21 Presence of amphibians 0-4 0-4 0-4 2 O (no evidence = 0; common, numerous types = max points) C 22 Presence of fish 0-4 0-4 0-4 1 (no evidence = 0; common, numerous types = max points) 23 Evidence of wildlife use 0-6 0-5 0-5 4 (no evidence = 0; abundant evidence = max points) Total Points Possible 100 100 100 TOTAL SCORE (also enter on first page) 82 * These characteristics are not assessed in coastal streams. USACE AID# Provide the following information for the stream reach under assessment. Hew5 Applicant's name: WREDCO attn: Sandy McLendon 3. Date of evaluation: 1/9/09 5. Name of stream: Hewitts Branch 7. Approximate drainage area: +/- 200 acres 9. Length of reach evaluated: 200 feet 2. Evaluator's name: Corev Novak 4. Time of evaluation: 12: 00 6. River basin: New River 8. Stream order: first 10. County: Onslow 11. Site coordinates (if known): prefer in decimal degrees. 12. Subdivision name (if any): n/a Latitude (ex. 34.872312): 34.8676 Longitude (ex. -77.556611): 77.4600 Method location determined (circle): GPS Topo Sheet Ortho (Aerial) Photo/GI Other GIS Other 13. Location of reach under evaluation (note nearby roads an an mar ?s and attach map identifying stream(s) location): (see GIS map showing data points) 14. Proposed channel work (if any): proposed channel preservation 15. Recent weather conditions: variable 16. Site conditions at time of visit: cold, sunny 17. Identify any special waterway classifications known: Section 10 Tidal Waters Essential Fisheries Habitat Trout Waters Outstanding Resource Waters Nutrient Sensitive Waters Water Supply Watershed (I-IV) 18. Is there a pond or lake located upstream of the evaluation point? YE NO yes, estimate the water surface area: 19. Does channel appear on USGS quad map? YES O 20. Does channel appear on USDA Soil Smvey? YES O 21. Estimated watershed land use: 0 % Residential 40 % Forested 22. Bankfull width: 3 feet 0 % Commercial 0 % Industrial 0 % Agricultural 60 % Cleared / Logged D-% Other ( ) 23. Bank height (from bed to top of bank): 6"-1' 24. Channel slope down center of stream: X Flat (0 to 2%) Gentle (2 to 41/o) Moderate (4 to 10%) Steep (>10%) 25. Channel sinuosity: Straight Occasional bends Frequent meander Very sinuous X Braided channel Instructions for completion of worksheet (located on page 2): Begin by determining the most appropriate ecoregion based on location, terrain, vegetation, stream classification, etc. Every characteristic must be scored using the same ecoregion. Assign points to each characteristic within the range shown for the ecoregion. Page 3 provides a brief description of how to review the characteristics identified in the worksheet. Scores should reflect an overall assessment of the stream reach under evaluation. If a characteristic cannot be evaluated due to site or weather conditions, enter 0 in the scoring box and provide an explanation in the comment section. Where there are obvious changes in the character of a stream under review (e.g., the stream flows from a pasture into a forest), the stream may be divided into smaller reaches that display more continuity, and a separate form used to evaluate each reach The total score assigned to a stream reach must range between 0 and 100, with a score of 100 representing a stream of the highest quality. Total Score (from reverse): 74 Comments: proposed area for stream preservation Evaluator's Signature Date 1/9/09 This channel evaluation form is intended to be used only as a guide to assist landowners and environmental professionals in gathering the data required by the United States Army Corps of Engineers to make a preliminary assessment of stream quality. The total score resulting from the completion of this form is subject to USACE approval and does not imply a particular mitigation ratio or requirement. Form subject to change - version 06/03. To Comment, please call 919-876-8441 x 26. DWQ# Site # (indicate on attached map) FE11 STREAM QUALITY ASSESSMENT WORKSHEET -AOQV STREAM QUALITY ASSESSMENT WORKSHEET # ECOREGION POINT RANGE CHARACTERISTICS SCORE Coastal Piedmont Mountain 1 Presence of flow / persistent pools in stream 0-5 0-4 0-5 3 (no flow or saturation = 0; strong flow = max points) 2 Evidence of past human alteration 0-6 0-5 0-5 5 (extensive alteration = 0; no alteration = max points) 3 Riparian zone 0-6 0-4 0-5 3 (no buffer = 0; contiguous, wide buffer = max points) 4 Evidence of nutrient or chemical discharges 0-5 0-4 0-4 5 (extensive discharges = 0; no discharges = max points) a 5 Groundwater discharge 0-3 0-4 0-4 3 U (no discharge = 0; springs, seeps, wetlands, etc. = max points) 6 Presence of adjacent floodplaln 0-4 0-4 0-2 4 (no floodplain = 0; extensive floodplain = max points) 7 Entrenchment / floodplain access 0-5 0-4 0-2 5 (deeply entrenched = 0; frequent flooding = max points) 8 Presence of adjacent wetlands 0-6 0-4 0-2 5 (no wetlands = 0; large adjacent wetlands = max points) 9 Channel sinuosity 0-5 0-4 0-3 5 (extensive channelization = 0; natural meander = max points) 10 Sediment input 0-5 0-4 0-4 5 (extensive deposition= 0; little or no sediment = max points) 11 Size & diversity of channel bed substrate NA* 0-4 0-5 N/A (fine, homogenous = 0; large, diverse sizes = max points) 12 Evidence of channel incision or widening 0-5 0-4 0-5 (deeply incised = 0; stable bed & banks = max points) 3 F'. 13 Presence of major bank failures 0-5 0-5 0-5 3 a (severe erosion = 0; no erosion, stable banks = max points) 14 Root depth and density on banks 0-3 0-4 0-5 3 H (no visible roots = 0; dense roots throughout = max points) 15 Impact by agriculture, livestock, or timber production 0-5 0-4 0-5 3 (substantial impact =0; no evidence = max points) 16 Presence of riffle-pool/ripple-pool complexes 0-3 0-5 0-6 2 (no riffles/ripples or pools = 0; well-developed = max points) 17 Habitat complexity 0-6 0-6 0-6 5 (little or no habitat = 0; frequent, varied habitats = max points) 18 Canopy coverage over streambed 0-5 0-5 0-5 3 (no shading vegetation = 0; continuous canopy = max points) 19 Substrate embeddedness NA* 0-4 0-4 N/A (deeply embedded = 0; loose structure = max) 20 Presence of stream invertebrates (see page 4) 0-4 0-5 0-5 3 (no evidence = 0; common, numerous types = max points) 21 Presence of amphibians 0-4 0-4 0-4 2 O (no evidence = 0; common, numerous types = max points) C 22 Presence of fish 0-4 0-4 0-4 0 (no evidence = 0; common, numerous types = max points) 23 Evidence of wildlife use 0-6 0-5 0-5 4 (no evidence = 0; abundant evidence = max points) Total Points Possible 100 100 100 TOTAL SCORE (also enter on first page) 74 * These characteristics are not assessed in coastal streams. USACE AID# Provide the following information for the stream reach under assessment. Huf2 Applicant's name: WREDCO attn: Sandy McLendon 3. Date of evaluation: 1/8/09 5. Name of stream: Hewitts Branch 7. Approximate drainage area: +/_ 200 acres 9. Length of reach evaluated: 200 feet 2. Evaluator's name: Corev Novak 4. Time of evaluation: 15: 00 6. River basin: New River 8. Stream order: first 10. County: Onslow 11. Site coordinates (if known): prefer in decimal degrees. 12. Subdivision name (if any): n/a Latitude (ex. 34.872312): 34.8575 Longitude (ex. -77.556611): 77.4552 Method location determined (circle): GPS Topo Sheet Ortho (Aerial) Photo/GI Other GIS Other 13. Location of reach under evaluation (note nearby roads an an mar ?s and attach map identifying stream(s) location): (see GIS map showing data points) 14. Proposed channel work (if any): proposed channel restoration 15. Recent weather conditions: mild 16. Site conditions at time of visit: warm, sunny 17. Identify any special waterway classifications known: Section 10 Tidal Waters Essential Fisheries Habitat Trout Waters Outstanding Resource Waters Nutrient Sensitive Waters Water Supply Watershed (I-IV) 18. Is there a pond or lake located upstream of the evaluation point? YE NO yes, estimate the water surface area: 19. Does channel appear on USGS quad map? YES O 20. Does channel appear on USDA Soil Smvey? YES O 21. Estimated watershed land use: 0 % Residential 60 % Forested 22. Bankfull width: 6 feet 0 % Commercial 0 % Industrial 0 % Agricultural 40 % Cleared / Logged D-% Other ( ) 23. Bank height (from bed to top of bank): 1' 24. Channel slope down center of stream: X Flat (0 to 2%) Gentle (2 to 41/o) Moderate (4 to 10%) Steep (>10%) 25. Channel sinuosity: Straight X Occasional bends Frequent meander Very sinuous Braided channel Instructions for completion of worksheet (located on page 2): Begin by determining the most appropriate ecoregion based on location, terrain, vegetation, stream classification, etc. Every characteristic must be scored using the same ecoregion. Assign points to each characteristic within the range shown for the ecoregion. Page 3 provides a brief description of how to review the characteristics identified in the worksheet. Scores should reflect an overall assessment of the stream reach under evaluation. If a characteristic cannot be evaluated due to site or weather conditions, enter 0 in the scoring box and provide an explanation in the comment section. Where there are obvious changes in the character of a stream under review (e.g., the stream flows from a pasture into a forest), the stream may be divided into smaller reaches that display more continuity, and a separate form used to evaluate each reach The total score assigned to a stream reach must range between 0 and 100, with a score of 100 representing a stream of the highest quality. Total Score (from reverse):47 Comments: proposed area for stream restoration spoil pile running along west side of ditch channel Evaluator's Signature Date 1/8/09 This channel evaluation form is intended to be used only as a guide to assist landowners and environmental professionals in gathering the data required by the United States Army Corps of Engineers to make a preliminary assessment of stream quality. The total score resulting from the completion of this form is subject to USACE approval and does not imply a particular mitigation ratio or requirement. Form subject to change - version 06/03. To Comment, please call 919-876-8441 x 26. DWQ# Site # (indicate on attached map) FE11 STREAM QUALITY ASSESSMENT WORKSHEET -AQP STREAM QUALITY ASSESSMENT WORKSHEET # ECOREGION POINT RANGE CHARACTERISTICS SCORE Coastal Piedmont Mountain 1 Presence of flow / persistent pools in stream 0-5 0-4 0-5 2 (no flow or saturation = 0; strong flow = max points) 2 Evidence of past human alteration 0-6 0-5 0-5 3 (extensive alteration = 0; no alteration = max points) 3 Riparian zone 0-6 0-4 0-5 4 (no buffer = 0; contiguous, wide buffer = max points) 4 Evidence of nutrient or chemical discharges 0-5 0-4 0-4 4 (extensive discharges = 0; no discharges = max points) a 5 Groundwater discharge 0-3 0-4 0-4 1 U (no discharge = 0; springs, seeps, wetlands, etc. = max points) 6 Presence of adjacent floodplaln 0-4 0-4 0-2 2 (no floodplain = 0; extensive floodplain = max points) 7 Entrenchment / floodplain access 0-5 0-4 0-2 2 (deeply entrenched = 0; frequent flooding = max points) 8 Presence of adjacent wetlands 0-6 0-4 0-2 3 (no wetlands = 0; large adjacent wetlands = max points) 9 Channel sinuosity 0-5 0-4 0-3 1 (extensive channelization = 0; natural meander = max points) 10 Sediment input 0-5 0-4 0-4 4 (extensive deposition= 0; little or no sediment = max points) 11 Size & diversity of channel bed substrate NA* 0-4 0-5 N/A (fine, homogenous = 0; large, diverse sizes = max points) 12 Evidence of channel incision or widening 0-5 0-4 0-5 (deeply incised = 0; stable bed & banks = max points) 3 F'. 13 Presence of major bank failures 0-5 0-5 0-5 3 a (severe erosion = 0; no erosion, stable banks = max points) 14 Root depth and density on banks 0-3 0-4 0-5 1 H (no visible roots = 0; dense roots throughout = max points) 15 Impact by agriculture, livestock, or timber production 0-5 0-4 0-5 4 (substantial impact =0; no evidence = max points) 16 Presence of riffle-pool/ripple-pool complexes 0-3 0-5 0-6 0 (no riffles/ripples or pools = 0; well-developed = max points) 17 Habitat complexity 0-6 0-6 0-6 2 (little or no habitat = 0; frequent, varied habitats = max points) 18 Canopy coverage over streambed 0-5 0-5 0-5 3 (no shading vegetation = 0; continuous canopy = max points) 19 Substrate embeddedness NA* 0-4 0-4 N/A (deeply embedded = 0; loose structure = max) 20 Presence of stream invertebrates (see page 4) 0-4 0-5 0-5 1 (no evidence = 0; common, numerous types = max points) 21 Presence of amphibians 0-4 0-4 0-4 1 O (no evidence = 0; common, numerous types = max points) C 22 Presence of fish 0-4 0-4 0-4 0 (no evidence = 0; common, numerous types = max points) 23 Evidence of wildlife use 0-6 0-5 0-5 3 (no evidence = 0; abundant evidence = max points) Total Points Possible 100 100 100 TOTAL SCORE (also enter on first page) 47 * These characteristics are not assessed in coastal streams. USACE AID# Provide the following information for the stream reach under assessment. Huf3 Applicant's name: WREDCO attn: Sandy McLendon 3. Date of evaluation: 1/9/09 5. Name of stream: Hewitts Branch 7. Approximate drainage area: +/_ 200 acres 9. Length of reach evaluated: 200 feet 2. Evaluator's name: Corev Novak 4. Time of evaluation: 14: 00 6. River basin: New River 8. Stream order: first 10. County: Onslow 11. Site coordinates (if known): prefer in decimal degrees. 12. Subdivision name (if any): n/a Latitude (ex. 34.872312): 34.8595 Longitude (ex. -77.556611): 77.4528 Method location determined (circle): GPS Topo Sheet Ortho (Aerial) Photo/GI Other GIS Other 13. Location of reach under evaluation (note nearby roads an an mar ?s and attach map identifying stream(s) location): (see GIS map showing data points) 14. Proposed channel work (if any): proposed channel restoration 15. Recent weather conditions: variable 16. Site conditions at time of visit: cold, sunny 17. Identify any special waterway classifications known: Section 10 Tidal Waters Essential Fisheries Habitat Trout Waters Outstanding Resource Waters Nutrient Sensitive Waters Water Supply Watershed (I-IV) 18. Is there a pond or lake located upstream of the evaluation point? YE NO yes, estimate the water surface area: 19. Does channel appear on USGS quad map? YES O 20. Does channel appear on USDA Soil Smvey? YES O 21. Estimated watershed land use: 0 % Residential 40 % Forested 22. Bankfull width: 2 0 % Commercial 0 % Industrial 0 % Agricultural 60 % Cleared / Logged D-% Other ( ) 23. Bank height (from bed to top of bank): 2.5' 24. Channel slope down center of stream: X Flat (0 to 2%) Gentle (2 to 41/o) Moderate (4 to 10%) Steep (>10%) 25. Channel sinuosity: X Straight Occasional bends Frequent meander Very sinuous Braided channel Instructions for completion of worksheet (located on page 2): Begin by determining the most appropriate ecoregion based on location, terrain, vegetation, stream classification, etc. Every characteristic must be scored using the same ecoregion. Assign points to each characteristic within the range shown for the ecoregion. Page 3 provides a brief description of how to review the characteristics identified in the worksheet. Scores should reflect an overall assessment of the stream reach under evaluation. If a characteristic cannot be evaluated due to site or weather conditions, enter 0 in the scoring box and provide an explanation in the comment section. Where there are obvious changes in the character of a stream under review (e.g., the stream flows from a pasture into a forest), the stream may be divided into smaller reaches that display more continuity, and a separate form used to evaluate each reach The total score assigned to a stream reach must range between 0 and 100, with a score of 100 representing a stream of the highest quality. Total Score (from reverse): 31 Comments: Evaluator's Signature Date 1/9/09 This channel evaluation form is intended to be used only as a guide to assist landowners and environmental professionals in gathering the data required by the United States Army Corps of Engineers to make a preliminary assessment of stream quality. The total score resulting from the completion of this form is subject to USACE approval and does not imply a particular mitigation ratio or requirement. Form subject to change - version 06/03. To Comment, please call 919-876-8441 x 26. DWQ# Site # (indicate on attached map) FE11 STREAM QUALITY ASSESSMENT WORKSHEET -AQP STREAM QUALITY ASSESSMENT WORKSHEET # ECOREGION POINT RANGE CHARACTERISTICS SCORE Coastal Piedmont Mountain 1 Presence of flow / persistent pools in stream 0-5 0-4 0-5 2 (no flow or saturation = 0; strong flow = max points) 2 Evidence of past human alteration 0-6 0-5 0-5 0 (extensive alteration = 0; no alteration = max points) 3 Riparian zone 0-6 0-4 0-5 1 (no buffer = 0; contiguous, wide buffer = max points) 4 Evidence of nutrient or chemical discharges 0-5 0-4 0-4 4 (extensive discharges = 0; no discharges = max points) a 5 Groundwater discharge 0-3 0-4 0-4 1 U (no discharge = 0; springs, seeps, wetlands, etc. = max points) 6 Presence of adjacent floodplaln 0-4 0-4 0-2 1 (no floodplain = 0; extensive floodplain = max points) 7 Entrenchment / floodplain access 0-5 0-4 0-2 0 (deeply entrenched = 0; frequent flooding = max points) 8 Presence of adjacent wetlands 0-6 0-4 0-2 1 (no wetlands = 0; large adjacent wetlands = max points) 9 Channel sinuosity 0-5 0-4 0-3 (extensive channelization = 0; natural meander = max points) 10 Sediment input 0-5 0-4 0-4 4 (extensive deposition= 0; little or no sediment = max points) 11 Size & diversity of channel bed substrate NA* 0-4 0-5 N/A (fine, homogenous = 0; large, diverse sizes = max points) 12 Evidence of channel incision or widening 0-5 0-4 0-5 (deeply incised = 0; stable bed & banks = max points) 0 F'. 13 Presence of major bank failures 0-5 0-5 0-5 4 a (severe erosion = 0; no erosion, stable banks = max points) 14 Root depth and density on banks 0-3 0-4 0-5 1 H (no visible roots = 0; dense roots throughout = max points) 15 Impact by agriculture, livestock, or timber production 0-5 0-4 0-5 2 (substantial impact =0; no evidence = max points) 16 Presence of riffle-pool/ripple-pool complexes 0-3 0-5 0-6 0 (no riffles/ripples or pools = 0; well-developed = max points) 17 Habitat complexity 0-6 0-6 0-6 1 (little or no habitat = 0; frequent, varied habitats = max points) 18 Canopy coverage over streambed 0-5 0-5 0-5 2 (no shading vegetation = 0; continuous canopy = max points) 19 Substrate embeddedness NA* 0-4 0-4 N/A (deeply embedded = 0; loose structure = max) 20 Presence of stream invertebrates (see page 4) 0-4 0-5 0-5 1 (no evidence = 0; common, numerous types = max points) 21 Presence of amphibians 0-4 0-4 0-4 1 O (no evidence = 0; common, numerous types = max points) C 22 Presence of fish 0-4 0-4 0-4 0 (no evidence = 0; common, numerous types = max points) 23 Evidence of wildlife use 0-6 0-5 0-5 4 (no evidence = 0; abundant evidence = max points) Total Points Possible 100 100 100 TOTAL SCORE (also enter on first page) 31 * These characteristics are not assessed in coastal streams. USACE AID# Provide the following information for the stream reach under assessment. Huf4 Applicant's name: WREDCO attn: Sandy McLendon 3. Date of evaluation: 1/13/09 5. Name of stream: Hewitts Branch 7. Approximate drainage area: +/_ 200 acres 9. Length of reach evaluated: 200 feet 2. Evaluator's name: Corev Novak 4. Time of evaluation: 15:45 6. River basin: New River 8. Stream order: first 10. County: Onslow 11. Site coordinates (if known): prefer in decimal degrees. 12. Subdivision name (if any): n/a Latitude (ex. 34.872312): 34.8577 Longitude (ex. -77.556611): 77.4539 Method location determined (circle): GPS Topo Sheet Ortho (Aerial) Photo/GI Other GIS Other 13. Location of reach under evaluation (note nearby roads an an mar ?s and attach map identifying stream(s) location): (see GIS map showing data points) 14. Proposed channel work (if any): proposed channel restoration 15. Recent weather conditions: variable 16. Site conditions at time of visit: cold, sunny 17. Identify any special waterway classifications known: Section 10 Tidal Waters Essential Fisheries Habitat Trout Waters Outstanding Resource Waters Nutrient Sensitive Waters Water Supply Watershed (I-IV) 18. Is there a pond or lake located upstream of the evaluation point? YE NO yes, estimate the water surface area: 19. Does channel appear on USGS quad map? YES O 21. Estimated watershed land use: 0 % Residential 40 % Forested 22. Bankfull width: 13' 20. Does channel appear on USDA Soil Survey? YE NO 0 % Commercial 0 % Industrial 0 % Agricultural 60 % Cleared / Logged D-% Other ( ) 23. Bank height (from bed to top of bank): 2.' 24. Channel slope down center of stream: X Flat (0 to 2%) Gentle (2 to 41/o) Moderate (4 to 10%) Steep (>10%) 25. Channel sinuosity: X Straight Occasional bends Frequent meander Very sinuous Braided channel Instructions for completion of worksheet (located on page 2): Begin by determining the most appropriate ecoregion based on location, terrain, vegetation, stream classification, etc. Every characteristic must be scored using the same ecoregion. Assign points to each characteristic within the range shown for the ecoregion. Page 3 provides a brief description of how to review the characteristics identified in the worksheet. Scores should reflect an overall assessment of the stream reach under evaluation. If a characteristic cannot be evaluated due to site or weather conditions, enter 0 in the scoring box and provide an explanation in the comment section. Where there are obvious changes in the character of a stream under review (e.g., the stream flows from a pasture into a forest), the stream may be divided into smaller reaches that display more continuity, and a separate form used to evaluate each reach The total score assigned to a stream reach must range between 0 and 100, with a score of 100 representing a stream of the highest quality. Total Score (from reverse): 37 Comments: Evaluator's Signature Date 1/9/09 This channel evaluation form is intended to be used only as a guide to assist landowners and environmental professionals in gathering the data required by the United States Army Corps of Engineers to make a preliminary assessment of stream quality. The total score resulting from the completion of this form is subject to USACE approval and does not imply a particular mitigation ratio or requirement. Form subject to change - version 06/03. To Comment, please call 919-876-8441 x 26. DWQ# Site # (indicate on attached map) FE11 STREAM QUALITY ASSESSMENT WORKSHEET -AQP STREAM QUALITY ASSESSMENT WORKSHEET # ECOREGION POINT RANGE CHARACTERISTICS SCORE Coastal Piedmont Mountain 1 Presence of flow / persistent pools in stream 0-5 0-4 0-5 3 (no flow or saturation = 0; strong flow = max points) 2 Evidence of past human alteration 0-6 0-5 0-5 1 (extensive alteration = 0; no alteration = max points) 3 Riparian zone 0-6 0-4 0-5 2 (no buffer = 0; contiguous, wide buffer = max points) 4 Evidence of nutrient or chemical discharges 0-5 0-4 0-4 4 (extensive discharges = 0; no discharges = max points) a 5 Groundwater discharge 0-3 0-4 0-4 2 U (no discharge = 0; springs, seeps, wetlands, etc. = max points) 6 Presence of adjacent floodplaln 0-4 0-4 0-2 2 (no floodplain = 0; extensive floodplain = max points) 7 Entrenchment / floodplain access 0-5 0-4 0-2 1 (deeply entrenched = 0; frequent flooding = max points) 8 Presence of adjacent wetlands 0-6 0-4 0-2 2 (no wetlands = 0; large adjacent wetlands = max points) 9 Channel sinuosity 0-5 0-4 0-3 1 (extensive channelization = 0; natural meander = max points) 10 Sediment input 0-5 0-4 0-4 4 (extensive deposition= 0; little or no sediment = max points) 11 Size & diversity of channel bed substrate NA* 0-4 0-5 N/A (fine, homogenous = 0; large, diverse sizes = max points) 12 Evidence of channel incision or widening 0-5 0-4 0-5 (deeply incised = 0; stable bed & banks = max points) 2 F'. 13 Presence of major bank failures 0-5 0-5 0-5 2 a (severe erosion = 0; no erosion, stable banks = max points) 14 Root depth and density on banks 0-3 0-4 0-5 1 H (no visible roots = 0; dense roots throughout = max points) 15 Impact by agriculture, livestock, or timber production 0-5 0-4 0-5 2 (substantial impact =0; no evidence = max points) 16 Presence of riffle-pool/ripple-pool complexes 0-3 0-5 0-6 0 (no riffles/ripples or pools = 0; well-developed = max points) 17 Habitat complexity 0-6 0-6 0-6 1 (little or no habitat = 0; frequent, varied habitats = max points) 18 Canopy coverage over streambed 0-5 0-5 0-5 2 (no shading vegetation = 0; continuous canopy = max points) 19 Substrate embeddedness NA* 0-4 0-4 N/A (deeply embedded = 0; loose structure = max) 20 Presence of stream invertebrates (see page 4) 0-4 0-5 0-5 1 (no evidence = 0; common, numerous types = max points) 21 Presence of amphibians 0-4 0-4 0-4 1 O (no evidence = 0; common, numerous types = max points) C 22 Presence of fish 0-4 0-4 0-4 0 (no evidence = 0; common, numerous types = max points) 23 Evidence of wildlife use 0-6 0-5 0-5 3 (no evidence = 0; abundant evidence = max points) Total Points Possible 100 100 100 TOTAL SCORE (also enter on first page) 37 * These characteristics are not assessed in coastal streams. USACE AID# Provide the following information for the stream reach under assessment. Applicant's name: WREDCO attn: Sandy McLendon 3. Date of evaluation: 1/13/09 5. Name of stream: Batchelors Deliqht Swam 7. Approximate drainage area: +/_ 200 acres 9. Length of reach evaluated: 200 feet 2. Evaluator's name: Corev Novak 4. Time of evaluation: 12: 00 6. River basin: New River 8. Stream order: First 10. County: Onslow 11. Site coordinates (if known): prefer in decimal degrees. 12. Subdivision name (if any): n/a Latitude (ex. 34.872312): 34.8575 Longitude (ex. -77.556611): 77.4396 Method location determined (circle): GPS Topo Sheet Ortho (Aeoto/GI Other GIS Other 13. Location of reach under evaluation (note nearby roads an ?s and atta ch map identifying stream(s) location): (see GIS map showing data points) 14. Proposed channel work (if any): proposed channel restoration 15. Recent weather conditions: variable 16. Site conditions at time of visit: cold, rain 17. Identify any special waterway classifications known: Section 10 Tidal Waters Essential Fisheries Habitat Trout Waters Outstanding Resource Waters Nutrient Sensitive Waters Water Supply Watershed (I-IV) 18. Is there a pond or lake located upstream of the evaluation point? YE NO yes, estimate the water surface area: 19. Does channel appear on USGS quad map? YES O 20. Does channel appear on USDA Soil Survey? YES O 21. Estimated watershed land use: 0 % Residential 22. Bankfull width: 2 40 % Forested 0 % Commercial 0 % Industrial 0 % Agricultural 60 % Cleared / Logged D-% Other ( ) 23. Bank height (from bed to top of bank): 6" 24. Channel slope down center of stream: X Flat (0 to 2%) Gentle (2 to 41/o) Moderate (4 to 10%) Steep (>10%) 25. Channel sinuosity: Straight Occasional bends X Frequent meander Very sinuous Braided channel Instructions for completion of worksheet (located on page 2): Begin by determining the most appropriate ecoregion based on location, terrain, vegetation, stream classification, etc. Every characteristic must be scored using the same ecoregion. Assign points to each characteristic within the range shown for the ecoregion. Page 3 provides a brief description of how to review the characteristics identified in the worksheet. Scores should reflect an overall assessment of the stream reach under evaluation. If a characteristic cannot be evaluated due to site or weather conditions, enter 0 in the scoring box and provide an explanation in the comment section. Where there are obvious changes in the character of a stream under review (e.g., the stream flows from a pasture into a forest), the stream may be divided into smaller reaches that display more continuity, and a separate form used to evaluate each reach The total score assigned to a stream reach must range between 0 and 100, with a score of 100 representing a stream of the highest quality. Total Score (from reverse):46 Comments: Evaluator's Signature Date 1/13/09 This channel evaluation form is intended to be used only as a guide to assist landowners and environmental professionals in gathering the data required by the United States Army Corps of Engineers to make a preliminary assessment of stream quality. The total score resulting from the completion of this form is subject to USACE approval and does not imply a particular mitigation ratio or requirement. Form subject to change - version 06/03. To Comment, please call 919-876-8441 x 26. DWQ# Site # (indicate on attached map) FE11 STREAM QUALITY ASSESSMENT WORKSHEET Bat -AQP STREAM QUALITY ASSESSMENT WORKSHEET # ECOREGION POINT RANGE CHARACTERISTICS SCORE Coastal Piedmont Mountain 1 Presence of flow / persistent pools in stream 0-5 0-4 0-5 0 (no flow or saturation = 0; strong flow = max points) 2 Evidence of past human alteration 0-6 0-5 0-5 4 (extensive alteration = 0; no alteration = max points) 3 Riparian zone 0-6 0-4 0-5 2 (no buffer = 0; contiguous, wide buffer = max points) 4 Evidence of nutrient or chemical discharges 0-5 0-4 0-4 1 (extensive discharges = 0; no discharges = max points) a 5 Groundwater discharge 0-3 0-4 0-4 3 U (no discharge = 0; springs, seeps, wetlands, etc. = max points) 6 Presence of adjacent floodplaln 0-4 0-4 0-2 3 (no floodplain = 0; extensive floodplain = max points) 7 Entrenchment / floodplain access 0-5 0-4 0-2 3 (deeply entrenched = 0; frequent flooding = max points) 8 Presence of adjacent wetlands 0-6 0-4 0-2 3 (no wetlands = 0; large adjacent wetlands = max points) 9 Channel sinuosity 0-5 0-4 0-3 (extensive channelization = 0; natural meander = max points) 3 10 Sediment input 0-5 0-4 0-4 5 (extensive deposition= 0; little or no sediment = max points) 11 Size & diversity of channel bed substrate NA* 0-4 0-5 N/A (fine, homogenous = 0; large, diverse sizes = max points) 12 Evidence of channel incision or widening 0-5 0-4 0-5 4 (deeply incised = 0; stable bed & banks = max points) F'. 13 Presence of major bank failures 0-5 0-5 0-5 4 a (severe erosion = 0; no erosion, stable banks = max points) 14 Root depth and density on banks 0-3 0-4 0-5 0 H (no visible roots = 0; dense roots throughout = max points) 15 Impact by agriculture, livestock, or timber production 0-5 0-4 0-5 3 (substantial impact =0; no evidence = max points) 16 Presence of riffle-pool/ripple-pool complexes 0-3 0-5 0-6 0 (no riffles/ripples or pools = 0; well-developed = max points) 17 Habitat complexity 0-6 0-6 0-6 1 (little or no habitat = 0; frequent, varied habitats = max points) 18 Canopy coverage over streambed 0-5 0-5 0-5 3 (no shading vegetation = 0; continuous canopy = max points) 19 Substrate embeddedness NA* 0-4 0-4 N/A (deeply embedded = 0; loose structure = max) 20 Presence of stream invertebrates (see page 4) 0-4 0-5 0-5 0 (no evidence = 0; common, numerous types = max points) 21 Presence of amphibians 0-4 0-4 0-4 0 O (no evidence = 0; common, numerous types = max points) C 22 Presence of fish 0-4 0-4 0-4 0 (no evidence = 0; common, numerous types = max points) 23 Evidence of wildlife use 0-6 0-5 0-5 4 (no evidence = 0; abundant evidence = max points) Total Points Possible 100 100 100 TOTAL SCORE (also enter on first page) 46 * These characteristics are not assessed in coastal streams. USACE AID# Provide the following information for the stream reach under assessment. Applicant's name: WREDCO attn: Sandy McLendon 3. Date of evaluation: 1/13/09 5. Name of stream: Batchelors Deliqht Swam 7. Approximate drainage area: +/_ 200 acres 9. Length of reach evaluated: 200 feet 2. Evaluator's name: Corev Novak 4. Time of evaluation: 13:30 6. River basin: New River 8. Stream order: Zero 10. County: Onslow 11. Site coordinates (if known): prefer in decimal degrees. 12. Subdivision name (if any): n/a Latitude (ex. 34.872312): 34.8561 Longitude (ex. -77.556611): 77.4405 Method location determined (circle): GPS Topo Sheet Ortho (Aeoto/GI Other GIS Other 13. Location of reach under evaluation (note nearby roads an ?s and atta ch map identifying stream(s) location): (see GIS map showing data points) 14. Proposed channel work (if any): proposed channel restoration 15. Recent weather conditions: variable 16. Site conditions at time of visit: cold, rain 17. Identify any special waterway classifications known: Section 10 Tidal Waters Essential Fisheries Habitat Trout Waters Outstanding Resource Waters Nutrient Sensitive Waters Water Supply Watershed (I-IV) 18. Is there a pond or lake located upstream of the evaluation point? YE NO yes, estimate the water surface area: 19. Does channel appear on USGS quad map? YES O 20. Does channel appear on USDA Soil Survey? YES O 21. Estimated watershed land use: 0 % Residential 22. Bankfull width: 50' 40 % Forested 0 % Commercial 0 % Industrial 0 % Agricultural 60 % Cleared / Logged D-% Other ( ) 23. Bank height (from bed to top of bank): 6" 24. Channel slope down center of stream: Flat (0 to 2%) X Gentle (2 to 41/o) Moderate (4 to 10%) Steep (>10%) 25. Channel sinuosity: Straight Occasional bends X Frequent meander Very sinuous Braided channel Instructions for completion of worksheet (located on page 2): Begin by determining the most appropriate ecoregion based on location, terrain, vegetation, stream classification, etc. Every characteristic must be scored using the same ecoregion. Assign points to each characteristic within the range shown for the ecoregion. Page 3 provides a brief description of how to review the characteristics identified in the worksheet. Scores should reflect an overall assessment of the stream reach under evaluation. If a characteristic cannot be evaluated due to site or weather conditions, enter 0 in the scoring box and provide an explanation in the comment section. Where there are obvious changes in the character of a stream under review (e.g., the stream flows from a pasture into a forest), the stream may be divided into smaller reaches that display more continuity, and a separate form used to evaluate each reach The total score assigned to a stream reach must range between 0 and 100, with a score of 100 representing a stream of the highest quality. Total Score (from reverse): 51 Comments: Swamp, there is no channel Evaluator's Signature Date 1/13/09 This channel evaluation form is intended to be used only as a guide to assist landowners and environmental professionals in gathering the data required by the United States Army Corps of Engineers to make a preliminary assessment of stream quality. The total score resulting from the completion of this form is subject to USACE approval and does not imply a particular mitigation ratio or requirement. Form subject to change - version 06/03. To Comment, please call 919-876-8441 x 26. DWQ# Site # (indicate on attached map) FE11 STREAM QUALITY ASSESSMENT WORKSHEET Bat -AQP STREAM QUALITY ASSESSMENT WORKSHEET # ECOREGION POINT RANGE CHARACTERISTICS SCORE Coastal Piedmont Mountain 1 Presence of flow / persistent pools in stream 0-5 0-4 0-5 2 (no flow or saturation = 0; strong flow = max points) 2 Evidence of past human alteration 0-6 0-5 0-5 3 (extensive alteration = 0; no alteration = max points) 3 Riparian zone 0-6 0-4 0-5 3 (no buffer = 0; contiguous, wide buffer = max points) 4 Evidence of nutrient or chemical discharges 0-5 0-4 0-4 4 (extensive discharges = 0; no discharges = max points) a 5 Groundwater discharge 0-3 0-4 0-4 2 U (no discharge = 0; springs, seeps, wetlands, etc. = max points) 6 Presence of adjacent floodplaln 0-4 0-4 0-2 3 (no floodplain = 0; extensive floodplain = max points) 7 Entrenchment / floodplain access 0-5 0-4 0-2 3 (deeply entrenched = 0; frequent flooding = max points) 8 Presence of adjacent wetlands 0-6 0-4 0-2 3 (no wetlands = 0; large adjacent wetlands = max points) 9 Channel sinuosity 0-5 0-4 0-3 4 (extensive channelization = 0; natural meander = max points) 10 Sediment input 0-5 0-4 0-4 4 (extensive deposition= 0; little or no sediment = max points) 11 Size & diversity of channel bed substrate NA* 0-4 0-5 N/A (fine, homogenous = 0; large, diverse sizes = max points) 12 Evidence of channel incision or widening 0-5 0-4 0-5 (deeply incised = 0; stable bed & banks = max points) 2 F'. 13 Presence of major bank failures 0-5 0-5 0-5 2 a (severe erosion = 0; no erosion, stable banks = max points) 14 Root depth and density on banks 0-3 0-4 0-5 2 H (no visible roots = 0; dense roots throughout = max points) 15 Impact by agriculture, livestock, or timber production 0-5 0-4 0-5 3 (substantial impact =0; no evidence = max points) 16 Presence of riffle-pool/ripple-pool complexes 0-3 0-5 0-6 0 (no riffles/ripples or pools = 0; well-developed = max points) 17 Habitat complexity 0-6 0-6 0-6 1 (little or no habitat = 0; frequent, varied habitats = max points) 18 Canopy coverage over streambed 0-5 0-5 0-5 4 (no shading vegetation = 0; continuous canopy = max points) 19 Substrate embeddedness NA* 0-4 0-4 N/A (deeply embedded = 0; loose structure = max) 20 Presence of stream invertebrates (see page 4) 0-4 0-5 0-5 0 (no evidence = 0; common, numerous types = max points) 21 Presence of amphibians 0-4 0-4 0-4 2 O (no evidence = 0; common, numerous types = max points) C 22 Presence of fish 0-4 0-4 0-4 0 (no evidence = 0; common, numerous types = max points) 23 Evidence of wildlife use 0-6 0-5 0-5 4 (no evidence = 0; abundant evidence = max points) Total Points Possible 100 100 100 TOTAL SCORE (also enter on first page) 51 * These characteristics are not assessed in coastal streams. USACE AID# Provide the following information for the stream reach under assessment. Applicant's name: WREDCO attn: Sandy McLendon 3. Date of evaluation: 1/13/09 5. Name of stream: Batchelors Deliqht Swam 7. Approximate drainage area: +/_ 200 acres 9. Length of reach evaluated: 200 feet 2. Evaluator's name: Corev Novak 4. Time of evaluation: 10: 30 6. River basin: New River 8. Stream order: First 10. County: Onslow 11. Site coordinates (if known): prefer in decimal degrees. 12. Subdivision name (if any): n/a Latitude (ex. 34.872312): 34.8538 Longitude (ex. -77.556611): 77.4377 Method location determined (circle): GPS Topo Sheet Ortho (Aeoto/GI Other GIS Other 13. Location of reach under evaluation (note nearby roads an ?s and atta ch map identifying stream(s) location): (see GIS map showing data points) 14. Proposed channel work (if any): proposed channel restoration 15. Recent weather conditions: variable 16. Site conditions at time of visit: cold, rain 17. Identify any special waterway classifications known: Section 10 Tidal Waters Essential Fisheries Habitat Trout Waters Outstanding Resource Waters Nutrient Sensitive Waters Water Supply Watershed (I-IV) 18. Is there a pond or lake located upstream of the evaluation point? YE NO yes, estimate the water surface area: 19. Does channel appear on USGS quad map? YES O 20. Does channel appear on USDA Soil Survey? YES O 21. Estimated watershed land use: 0 % Residential 22. Bankfull width: 7 40 % Forested 0 % Commercial 0 % Industrial 0 % Agricultural 60 % Cleared / Logged D-% Other ( ) 23. Bank height (from bed to top of bank): 3" 24. Channel slope down center of stream: Flat (0 to 2%) X Gentle (2 to 41/o) Moderate (4 to 10%) Steep (>10%) 25. Channel sinuosity: Straight X Occasional bends Frequent meander Very sinuous Braided channel Instructions for completion of worksheet (located on page 2): Begin by determining the most appropriate ecoregion based on location, terrain, vegetation, stream classification, etc. Every characteristic must be scored using the same ecoregion. Assign points to each characteristic within the range shown for the ecoregion. Page 3 provides a brief description of how to review the characteristics identified in the worksheet. Scores should reflect an overall assessment of the stream reach under evaluation. If a characteristic cannot be evaluated due to site or weather conditions, enter 0 in the scoring box and provide an explanation in the comment section. Where there are obvious changes in the character of a stream under review (e.g., the stream flows from a pasture into a forest), the stream may be divided into smaller reaches that display more continuity, and a separate form used to evaluate each reach The total score assigned to a stream reach must range between 0 and 100, with a score of 100 representing a stream of the highest quality. Total Score (from reverse):41 Comments: Evaluator's Signature Date 1/13/09 This channel evaluation form is intended to be used only as a guide to assist landowners and environmental professionals in gathering the data required by the United States Army Corps of Engineers to make a preliminary assessment of stream quality. The total score resulting from the completion of this form is subject to USACE approval and does not imply a particular mitigation ratio or requirement. Form subject to change - version 06/03. To Comment, please call 919-876-8441 x 26. DWQ# Site # (indicate on attached map) FE11 STREAM QUALITY ASSESSMENT WORKSHEET Ba3 -AQP STREAM QUALITY ASSESSMENT WORKSHEET # ECOREGION POINT RANGE CHARACTERISTICS SCORE Coastal Piedmont Mountain 1 Presence of flow / persistent pools in stream 0-5 0-4 0-5 4 (no flow or saturation = 0; strong flow = max points) 2 Evidence of past human alteration 0-6 0-5 0-5 1 (extensive alteration = 0; no alteration = max points) 3 Riparian zone 0-6 0-4 0-5 3 (no buffer = 0; contiguous, wide buffer = max points) 4 Evidence of nutrient or chemical discharges 0-5 0-4 0-4 4 (extensive discharges = 0; no discharges = max points) a 5 Groundwater discharge 0-3 0-4 0-4 1 U (no discharge = 0; springs, seeps, wetlands, etc. = max points) 6 Presence of adjacent floodplaln 0-4 0-4 0-2 2 (no floodplain = 0; extensive floodplain = max points) 7 Entrenchment / floodplain access 0-5 0-4 0-2 2 (deeply entrenched = 0; frequent flooding = max points) 8 Presence of adjacent wetlands 0-6 0-4 0-2 3 (no wetlands = 0; large adjacent wetlands = max points) 9 Channel sinuosity 0-5 0-4 0-3 1 (extensive channelization = 0; natural meander = max points) 10 Sediment input 0-5 0-4 0-4 4 (extensive deposition= 0; little or no sediment = max points) 11 Size & diversity of channel bed substrate NA* 0-4 0-5 N/A (fine, homogenous = 0; large, diverse sizes = max points) 12 Evidence of channel incision or widening 0-5 0-4 0-5 (deeply incised = 0; stable bed & banks = max points) 0 F'. 13 Presence of major bank failures 0-5 0-5 0-5 2 a (severe erosion = 0; no erosion, stable banks = max points) 14 Root depth and density on banks 0-3 0-4 0-5 1 H (no visible roots = 0; dense roots throughout = max points) 15 Impact by agriculture, livestock, or timber production 0-5 0-4 0-5 3 (substantial impact =0; no evidence = max points) 16 Presence of riffle-pool/ripple-pool complexes 0-3 0-5 0-6 0 (no riffles/ripples or pools = 0; well-developed = max points) 17 Habitat complexity 0-6 0-6 0-6 1 (little or no habitat = 0; frequent, varied habitats = max points) 18 Canopy coverage over streambed 0-5 0-5 0-5 3 (no shading vegetation = 0; continuous canopy = max points) 19 Substrate embeddedness NA* 0-4 0-4 N/A (deeply embedded = 0; loose structure = max) 20 Presence of stream invertebrates (see page 4) 0-4 0-5 0-5 1 (no evidence = 0; common, numerous types = max points) 21 Presence of amphibians 0-4 0-4 0-4 1 O (no evidence = 0; common, numerous types = max points) C 22 Presence of fish 0-4 0-4 0-4 0 (no evidence = 0; common, numerous types = max points) 23 Evidence of wildlife use 0-6 0-5 0-5 4 (no evidence = 0; abundant evidence = max points) Total Points Possible 100 100 100 TOTAL SCORE (also enter on first page) 41 * These characteristics are not assessed in coastal streams. USACE AID# Provide the following information for the stream reach under assessment. Applicant's name: WREDCO attn: Sandy McLendon 3. Date of evaluation: 1/13/09 5. Name of stream: Batchelors Deliqht Swam 7. Approximate drainage area: +/_ 200 acres 9. Length of reach evaluated: 200 feet 2. Evaluator's name: Corev Novak 4. Time of evaluation: 15: 00 6. River basin: New River 8. Stream order: First 10. County: Onslow 11. Site coordinates (if known): prefer in decimal degrees. 12. Subdivision name (if any): n/a Latitude (ex. 34.872312): 34.8533 Longitude (ex. -77.556611): 77.4394 Method location determined (circle): GPS Topo Sheet Ortho (Aeoto/GI Other GIS Other 13. Location of reach under evaluation (note nearby roads an ?s and atta ch map identifying stream(s) location): (see GIS map showing data points) 14. Proposed channel work (if any): proposed channel restoration 15. Recent weather conditions: variable 16. Site conditions at time of visit: cold, rain 17. Identify any special waterway classifications known: Section 10 Tidal Waters Essential Fisheries Habitat Trout Waters Outstanding Resource Waters Nutrient Sensitive Waters Water Supply Watershed (I-IV) 18. Is there a pond or lake located upstream of the evaluation point? YE NO yes, estimate the water surface area: 19. Does channel appear on USGS quad map? YES O 20. Does channel appear on USDA Soil Survey? YES O 21. Estimated watershed land use: 0 % Residential 22. Bankfull width: 6 40 % Forested 0 % Commercial 0 % Industrial 0 % Agricultural 60 % Cleared / Logged D-% Other ( ) 23. Bank height (from bed to top of bank): 3" 24. Channel slope down center of stream: Flat (0 to 2%) X Gentle (2 to 41/o) Moderate (4 to 10%) Steep (>10%) 25. Channel sinuosity: Straight Occasional bends Frequent meander X Very sinuous Braided channel Instructions for completion of worksheet (located on page 2): Begin by determining the most appropriate ecoregion based on location, terrain, vegetation, stream classification, etc. Every characteristic must be scored using the same ecoregion. Assign points to each characteristic within the range shown for the ecoregion. Page 3 provides a brief description of how to review the characteristics identified in the worksheet. Scores should reflect an overall assessment of the stream reach under evaluation. If a characteristic cannot be evaluated due to site or weather conditions, enter 0 in the scoring box and provide an explanation in the comment section. Where there are obvious changes in the character of a stream under review (e.g., the stream flows from a pasture into a forest), the stream may be divided into smaller reaches that display more continuity, and a separate form used to evaluate each reach The total score assigned to a stream reach must range between 0 and 100, with a score of 100 representing a stream of the highest quality. Total Score (from reverse): 72 Comments: Evaluator's Signature Date 1/13/09 This channel evaluation form is intended to be used only as a guide to assist landowners and environmental professionals in gathering the data required by the United States Army Corps of Engineers to make a preliminary assessment of stream quality. The total score resulting from the completion of this form is subject to USACE approval and does not imply a particular mitigation ratio or requirement. Form subject to change - version 06/03. To Comment, please call 919-876-8441 x 26. DWQ# Site # (indicate on attached map) FE11 STREAM QUALITY ASSESSMENT WORKSHEET Ba4 -AQP STREAM QUALITY ASSESSMENT WORKSHEET # ECOREGION POINT RANGE CHARACTERISTICS SCORE Coastal Piedmont Mountain 1 Presence of flow / persistent pools in stream 0-5 0-4 0-5 5 (no flow or saturation = 0; strong flow = max points) 2 Evidence of past human alteration 0-6 0-5 0-5 3 (extensive alteration = 0; no alteration = max points) 3 Riparian zone 0-6 0-4 0-5 3 (no buffer = 0; contiguous, wide buffer = max points) 4 Evidence of nutrient or chemical discharges 0-5 0-4 0-4 5 (extensive discharges = 0; no discharges = max points) a 5 Groundwater discharge 0-3 0-4 0-4 2 U (no discharge = 0; springs, seeps, wetlands, etc. = max points) 6 Presence of adjacent floodplaln 0-4 0-4 0-2 3 (no floodplain = 0; extensive floodplain = max points) 7 Entrenchment / floodplain access 0-5 0-4 0-2 3 (deeply entrenched = 0; frequent flooding = max points) 8 Presence of adjacent wetlands 0-6 0-4 0-2 4 (no wetlands = 0; large adjacent wetlands = max points) 9 Channel sinuosity 0-5 0-4 0-3 4 (extensive channelization = 0; natural meander = max points) 10 Sediment input 0-5 0-4 0-4 5 (extensive deposition= 0; little or no sediment = max points) 11 Size & diversity of channel bed substrate NA* 0-4 0-5 N/A (fine, homogenous = 0; large, diverse sizes = max points) 12 Evidence of channel incision or widening 0-5 0-4 0-5 (deeply incised = 0; stable bed & banks = max points) 3 F'. 13 Presence of major bank failures 0-5 0-5 0-5 3 a (severe erosion = 0; no erosion, stable banks = max points) 14 Root depth and density on banks 0-3 0-4 0-5 3 H (no visible roots = 0; dense roots throughout = max points) 15 Impact by agriculture, livestock, or timber production 0-5 0-4 0-5 4 (substantial impact =0; no evidence = max points) 16 Presence of riffle-pool/ripple-pool complexes 0-3 0-5 0-6 2 (no riffles/ripples or pools = 0; well-developed = max points) 17 Habitat complexity 0-6 0-6 0-6 5 (little or no habitat = 0; frequent, varied habitats = max points) 18 Canopy coverage over streambed 0-5 0-5 0-5 4 (no shading vegetation = 0; continuous canopy = max points) 19 Substrate embeddedness NA* 0-4 0-4 N/A (deeply embedded = 0; loose structure = max) 20 Presence of stream invertebrates (see page 4) 0-4 0-5 0-5 3 (no evidence = 0; common, numerous types = max points) 21 Presence of amphibians 0-4 0-4 0-4 2 O (no evidence = 0; common, numerous types = max points) C 22 Presence of fish 0-4 0-4 0-4 1 (no evidence = 0; common, numerous types = max points) 23 Evidence of wildlife use 0-6 0-5 0-5 5 (no evidence = 0; abundant evidence = max points) Total Points Possible 100 100 100 TOTAL SCORE (also enter on first page) 72 * These characteristics are not assessed in coastal streams. APPENDIX E. REFERENCE REACH STUDY/HEC-RAS MODELING Morphological Characteristics of Bachelors Delight: HM-1 and Reference Reach: Bachelors Delight: HE-1 County: Onslow County, INC Design by: CLS Checked by: RVS ITEM Existing Conditions Existing Conditions Reference Reach Proposed Conditions Proposed Conditions LOCATION HE-1 Up HE-1 Down BD-2 - Downstream of Soil Road HE-1 Up HE-1 Down STREAM TYPE No stream associated. G5 - B5 E5 E5 E5 DRAINAGE AREA, Ac - Sq Mi 179 Ac - 0.28 S Mi 227 Ac - 0.35 S Mi 83 Ac - 0.13 S Mi 83 Ac - 0.13 S Mi 182 Ac - 0.28 S Mi BANKFULL DISCHARGE, cfs 5.8 cfs 1.0 cfs 2.0 cfs 4.4 cfs BANKFULL X-SECTION AREA (Abkf), ft2 6.09 ft2 2.6 ft2 2.9 ft2 8.4 ftZ BANKFULL MEAN VELOCITY, fps 0.95 fps 0.4 fps 0.6 fps 0.8 fps BANKFULL WIDTH (Wbkf), ft The valley's natural 5.4 ft 4.1 ft 6.0 ft 8.0 ft BANKFULL MEAN DEPTH (dbkf), ft drainage course has been 1.13 ft 0.63 ft 0.57 ft 0.76 ft WIDTH/DEPTH RATIO W d ( bkf/ bkf) routed to roadside dithces, therefore no data could be 4.8 6.5 10.5 10.5 BANKFULL MAX DEPTH (d_o, ft collected on channel 1.31 ft 0.88 ft 0.86 ft 1.14 ft BANK HEIGHT RATIO dimension. 2.00 1.00 1.00 1.00 TYPICAL BANK HEIGHT ABOVE BANKFULL 2.62 ft 0.88 ft 0.86 ft 1.14 ft WIDTH Flood-Prone Area (Wfpa), ft 11.6 ft 50.0 ft 50.00 ft 50.00 ft ENTRENCHMENT RATIO (ER) 2.15 12.2 8.3 6.3 MEANDER LENGTH (Lm), ft 12.6 - 12.6 ft 18.0 - 60.0 ft 24.0 - 80.0 ft RATIO OF Lm TO Wbkf The valley's natural Stream has been 3.1 - 3.1 3.0 - 10.0 3.0 - 10.0 RADIUS OF CURVATURE, ft drainage course has been channelized and h th t i ht d th 2.0 ft 12.0 - 18.0 ft 16.0 - 24.0 ft RATIO OF Rc TOW bkf routed to roadside dithces, therefore no data could be e s ra g ene roug vay displaying no natural 0.5- 1.1 2.0 - 3.0 2.0 - 3.0 BELT WIDTH, ft collected on channel , meander pattern. 9.6- 9.6 ft 10.1 - 34.4 ft 13.5 - 45.9 ft MEANDER WIDTH RATIO pattern. 2.3- 2.3 1.7 - 5.7 1.7 - 5.7 SINUOSITY (K) 1.02 1.25 1.30 1.17 VALLEY SLOPE, ft/ft 0.0028 ft/ft* 0.0049 ft/ft* 0.0027 ft/ft 0.0028 ft/ft 0.0049 ft/ft AVERAGE SLOPE (S), ft/ft 0.0010 ft/ft** 0.0024 ft/ft 0.0012 ft/ft 0.0015 ft/ft RIFFLE SLOPE, ft/ft 0.0010 ft/ft 0.0136 ft/ft 0.0014 ft/ft 0.0018 ft/ft RATIO OF RIFFLE SLOPE TO AVERAGE SLOPE 1.0 5.7 1.2 1.2 POOL SLOPE, ft/ft 0.0010 ft/ft 0.0000 ft/ft 0.0000 ft/ft RATIO OF POOL SLOPE TO AVERAGE SLOPE P l ti l d 0.4 0.0 0.0 MAX POOL DEPTH, ft The valley's natural oo cross-sec ona an lon itudinal data not 1.26 ft 1.14 ft 1.52 ft IO POOL DEPTH TO AVERAGE RAT BANKFUL L DEPTH drainage course has been routed to roadside dithces, g collected because the channel appears to have 2 0 2.0 2.0 POOL WIDTH, ft therefore no data could be collected on channel slope and feature spacing. little to no naturally forming pools because the channel has been straightned 7.18 ft 6.60 ft 8.80 ft RATIO OF POOL WIDTH TO BANKFULL WIDTH through the valley. 1.76 1.10 1.10 POOL TO POOL SPACING, ft 0.00 -1 0.00 ft 3.3 - 12.9 ft 6.0 - 30.0 ft 8.0 - 40.0 ft RATIO OF POOL TO POOL SPACING TO 11BANKFULLWIDTH 0.00-1 0.00 0.8- 3.2 1.0 - 5.0 1.0 -1 5.0 * Valley Slope, and Sinuosity were taken from topographical data obtained on the entire site for existing conditions (i.e. data was not taken along reach lengths). ** Average Slope was taken along a reach length for existing conditions. Morphological Characteristics of Bachelors Delight: HU-1 and Reference Reach: Bachelors Delight: HU-1 County: Onslow County, NC Design by: CLS Checked by: RVS ITEM Existing Conditions Reference Reach Reference Reach Proposed Conditions Proposed Conditions LOCATION HU-1 BD-2 - Downstream of Soil Road BD-5 Zero Order Bachelors Delight: HU-1 Zero Order Channel Bachelors Delight: HU-1 Single Thread Channel STREAM TYPE E5 E5 Zero Order Zero Order E5 DRAINAGE AREA, Ac - Sq Mi 64 Ac - 0.10 Sq Mi 83 Ac - 0.13 Sq Mi 20 Ac - 0.03 Sq Mi 75 Ac - 0.12 Sq Mi 157 Ac - 0.25 Sq Mi BANKFULL DISCHARGE, cfs 2.9 cfs 1.0 cfs BD-5's remnant, realtively 3.0 cfs BANKFULL X-SECTION AREA (Abkf), fz 2.79 fz 2.58 fz undisturbed zero order Existing ditch/channel to b fill d t i ti d 7.3 fz BANKFULL MEAN VELOCITY, fps 1.03 fps 0.40 fps channel is indicative of a e e o ex s ng groun at low point of valley. 0.8 fps BAN KFULL WIDTH ( °bkf), ft 4.7 ft 4.1 ft natural zero order stream. 7.0 ft VALLEY TOE OF SLOPE WIDTH NA NA 52.0 ft 15.0 ft NA BANKFULL MEAN DEPTH (dbkf), ft 0.59 ft 0.63 ft 0.67 ft WIDTH/DEPTH RATIO ( °bkddbkf) 8.0 6.5 No meander pattern is to 10.5 BANKFULL MAX DEPTH (dm_), ft 0.82 ft 0.88 ft be constructed for zero d h l 1.00 ft BANK HEIGHT RATIO 1.10 1.00 or er c anne . Restoration of the 1.00 TYPICAL BANK HEIGHT ABOVE BANKFULL 0.90 ft 0.88 ft s zero valley s order l i i t di l floodplain's natural 1.00 ft WIDTH Flood-Prone Area (Wfpa), ft 13.5 ft 50.0 ft s var ous ow po n s sp ay where saturation and groundwater hydrology grou 25.00 ft ENTRENCHMENT RATIO (ER) 2.87 12.22 overland flows have and surface water flows i t i t d 3.6 MEANDER LENGTH (Lm), ft 13- 13 ft caused depressions, n even s) s expec e (ra to create natural braided 21.0 - 70.0 ft RATIO OF Lm TO Wbkf Stream has been 3.1 - 3.1 however, no discernable h l h f d t low points throughout the 3.0 - 10.0 channelized and t i ht d th h th c anne as orme o convey valley. Proposed valley 14.0 - 21.0 ft RATIO OF Rc TOW bkf s ra g ene roug e vall displaying no natural y 0.5- 1.1 width was determined i t f th 2.0 - 3.0 BELT WIDTH, ft , meander pattern. 9.60- 9.60 ft us ng con ours o e valley floor following ditch 11.8 - 40.2 ft MEANDER WIDTH RATIO 2.35 - 2.35 ft fill. 1.7 - 5.7 SINUOSITY (K) 1.03 1.25 1.20 VALLEY SLOPE, ft/ft 0.0038 ft/ft* 0.0027 ft/ft 0.0017 ft/ft 0.0038 ft/ft 0.0038 ft/ft AVERAGE SLOPE (S), ft/ft 0.0014 ft/ft** 0.0024 ft/ft 0.0016 ft/ft RIFFLE SLOPE, ft/ft 0.0058 ft/ft 0.0136 ft/ft 0.0019 ft/ft RATIO OF RIFFLE SLOPE TO AVERAGE SLOPE 4.2 5.7 1.2 POOL SLOPE, ft/ft 0.0007 ft/ft 0.0010 ft/ft 0.0000 ft/ft RATIO OF POOL SLOPE TO AVERAGE SLOPE 0.5 0.4 0.0 MAX POOL DEPTH, ft 1.32 ft 1.26 ft 1.33 ft RATIO OF POOL DEPTH TO AVERAGE BANKFULL DEPTH 2.2 2.0 2.0 POOL WIDTH, ft 7.2 ft 7.2 ft 7.70 ft RATIO OF POOL WIDTH TO BANKFULL WIDTH 1.5 1.8 1.10 POOL TO POOL SPACING, ft 43.42 - 43.42 ft 3.34- 12.94 ft 7.0 - 35.0 ft RATIO OF POOL TO POOL SPACING TO BANKFULL WIDTH 9.24- 9.24 0.82-1 3.16 1.0 - 5.0 * Valley Slope, and Sinuosity were taken from topographical data obtained on the entire site for existing conditions (i.e. data was not taken along reach lengths). ** Average Slope was taken along a reach length for existing conditions. Morphological Characteristics of Bachelors Delight: HU-2 and Reference Reach: Bachelors Delight: HU-2 County: Onslow County, INC Design by: CLS Checked by: RVS ITEM Existing Conditions Reference Reach Proposed Conditions LOCATION HU-2 BD-5 Zero Order Bachelors Delight: HU-2 STREAM TYPE G-5 Zero Order Zero Order DRAINAGE AREA, Ac - Sq Mi 55 Ac - 0.09 S Mi 20 Ac - 0.03 S Mi 55 Ac - 0.09 S Mi BANKFULL DISCHARGE, cfs 1.4 cfs BD-5's remnant realtively BANKFULL X-SECTION AREA (Abkf), ft2 1.05 ft2 , undisturbed zero order Existing ditch/channel to be fill d t i ti d t l BANKFULL MEAN VELOCITY, fps 1.30 fps channel is indicative of a e o ex s ng groun a ow point of valley. BANKFULL WIDTH (Wbkf), ft 3.3 ft natural zero order stream. VALLEY TOE OF SLOPE WIDTH 15.0 ft 52.0 ft 15.0 ft BANKFULL MEAN DEPTH (dbkf), ft 0.32 ft WIDTH/DEPTH RATIO (Wbkddbkf) 10.3 BANKFULL MAX DEPTH (dm), ft 0.54 ft No meander pattern is to be constructed for zero order BANK HEIGHT RATIO 3.52 channel. Restoration of the TYPICAL BANK HEIGHT ABOVE BANKFULL 1.90 ft dis la s oivalleynts s va zero rious order low la s floodplain's natural WIDTH Flood-Prone Area (Wfp,), ft 4.6 ft p p y p where saturation and groundwater hydrology and ENTRENCHMENT RATIO (ER) 1.39 overland flows have surface water flows (rain t i t d t t MEANDER LENGTH (Lm), ft caused depressions, even s) s expec e o crea e natural braided low points RATIO OF Lm TO Wbkf Stream has been however, no discernable h l h f d t throughout the valley. RADIUS OF CURVATURE, ft c th and d th t i ht h th t i ht c anne as orme o convey flow. Proposed valley width was RATIO OF Rc TO Wbkf r r s ra g eneoug e s ra g ene vally displaying no natural determined using contours of th ll fl f ll i dit h BELT WIDTH, ft , meander pattern. e va ey oor o ow ng c fill MEANDER WIDTH RATIO . SINUOSITY (K) 1.01 VALLEY SLOPE, ft/ft 0.0044 ft/ft* 0.0017 0.0044 AVERAGE SLOPE (S), ft/ft 0.0060 ft/ft RIFFLE SLOPE, ft/ft 0.0060 ft/ft RATIO OF RIFFLE SLOPE TO AVERAGE SLOPE 1.0 POOL SLOPE, ft/ft RATIO OF POOL SLOPE TO AVERAGE SLOPE MAX POOL DEPTH, ft Pool cross-sectional and RATIO OF POOL DEPTH TO AVERAGE BANKFULL DEPTH longitudinal data not collected because the POOL WIDTH, ft channel appears to have little to no naturally forming pools because the RATIO OF POOL WIDTH TO BANKFULL WIDTH channel has been straightned through the valley. POOL TO POOL SPACING, ft RATIO OF POOL TO POOL SPACING TO BANKFULL WIDTH * Valley Slope, and Sinuosity were taken from topographical data obtained on the entire site for existing conditions (i.e. data was not taken along reach lengths). ** Average Slope was taken along a reach length for existing conditions. Morphological Characteristics of Bachelors Delight: BD-2 and Reference Reach: Bachelors Delight: 1313-2 County: Onslow County, INC Design by: CLS Checked by: RVS ITEM Existing Conditions Reference Reach Proposed Conditions LOCATION BD-2 BD-5 Zero Order Bachelors Delight: BD-2 STREAM TYPE F-5 Zero Order Zero Order DRAINAGE AREA, Ac - Sq Mi 64 Ac - 0.10 S Mi 20 Ac - 0.03 S Mi 65 Ac - 0.10 S Mi BANKFULL DISCHARGE, cfs 0.4 cfs BD-5's remnant realtively BANKFULL X-SECTION AREA (Abkf), ft2 1.70 ft2 , undisturbed zero order Existing ditch/channel to be fill d t i ti d t l BANKFULL MEAN VELOCITY, fps 0.26 fps channel is indicative of a e o ex s ng groun a ow point of valley. BANKFULL WIDTH (Wbkf), ft 5.2 ft natural zero order stream. VALLEY TOE OF SLOPE WIDTH ft 52.0 ft 30.0 ft BANKFULL MEAN DEPTH (dbkf), ft 0.33 ft WIDTH/DEPTH RATIO (Wbkddbkf) 15.8 BANKFULL MAX DEPTH (dm), ft 0.60 ft No meander pattern is to be constructed for zero order BANK HEIGHT RATIO 3.33 channel. Restoration of the TYPICAL BANK HEIGHT ABOVE BANKFULL 2.00 ft dis la s oivalleynts s va zero rious order low la s floodplain's natural WIDTH Flood-Prone Area (Wfp,), ft 6.6 ft p p y p where saturation and groundwater hydrology and ENTRENCHMENT RATIO (ER) 1.27 overland flows have surface water flows (rain t i t d t t MEANDER LENGTH (Lm), ft caused depressions, even s) s expec e o crea e natural braided low points RATIO OF Lm TO Wbkf Stream has been however, no discernable h l h f d t throughout the valley. RADIUS OF CURVATURE, ft channelized and t i ht d th h th c anne as orme o convey flow. Proposed valley width was RATIO OF Rc TO Wbkf s ra g ene roug e displaying no natural vall Y determined using contours of th ll fl f ll i dit h BELT WIDTH, ft . meander pattern. e va ey oor o ow ng c fill MEANDER WIDTH RATIO . SINUOSITY (K) 1.00 VALLEY SLOPE, ft/ft 0.0002 ft/ft* 0.00171 1 AVERAGE SLOPE (S), ft/ft 0.0002 ft/ft** RIFFLE SLOPE, ft/ft 0.0002 ft/ft RATIO OF RIFFLE SLOPE TO AVERAGE SLOPE 1.0 POOL SLOPE, ft/ft RATIO OF POOL SLOPE TO AVERAGE SLOPE MAX POOL DEPTH, ft Pool cross-sectional and RATIO OF POOL DEPTH TO AVERAGE BANKFULL DEPTH longitudinal data not collected because the POOL WIDTH, ft channel appears to have little to no naturally forming pools because the RATIO OF POOL WIDTH TO BANKFULL WIDTH channel has been straightned through the valley. POOL TO POOL SPACING, ft RATIO OF POOL TO POOL SPACING TO BANKFULL WIDTH * Valley Slope, and Sinuosity were taken from topographical data obtained on the entire site for existing conditions (i.e. data was not taken along reach lengths). ** Average Slope was taken along a reach length for existing conditions. Morphological Characteristics of Bachelors Delight: BD-4Aa, BD-4Ab, BD-5A and Reference Reach: Bachelors Delight: BD-4Aa, BD-4Ab, and 5A County: Robeson County, NC Design by: CLS Checked by: RVS ITEM Existing Conditions Existing Conditions Existing Conditions Reference Reach Proposed Conditions Proposed Conditions Proposed Conditions LOCATION BD-4Aa BD-4Ab BD-5A BD-5 Zero Order Bachelors Delight: BD- 4Aa Bachelors Delight: BD- 4Ab Bachelors Delight - BD-5a STREAM TYPE Agricultural Field Agricultural Field Agricultural Field Zero Order Zero Order Zero Order HEADWATER CHANNEL DRAINAGE AREA, Ac - Sq Mi 24.32 Ac 0.04 Sq Mi 7.68 Ac 0.01 Sq Mi 9.86 Ac 0.02 Sq Mi 20 Ac - 0.03 Sq Mi 24 Ac - 0.04 Sq Mi 8 Ac -10.01 Sq Mi 10 Ac -10.02 Sq Mi BANKFULL DISCHARGE, cfs BD-5's remnant, realtively ( bit) z BANKFULL X-SECTION AREA A ft undisturbed zero order Existing ditch/channel to b fill d t i ti d Existing ditch/channel to b fill d t i ti d Existing ditch/channel to be fill d t i ti d t t BANKFULL MEAN VELOCITY, fps channel is indicative of a e e o ex s ng groun at low point of valley. e e o ex s ng groun at low point of valley. e o ex s ng groun a o point of valley. BANKFULL WIDTH (Wbkf), ft natural zero order stream. VALLEY TOE OF SLOPE WIDTH 52.0 ft 30.0 ft 30.0 ft 30.0 ft BANKFULL MEAN DEPTH (dbkf), ft WIDTH/DEPTH RATIO (Wb,/dbl) Existing conditions are Existing conditions are Existing conditions are No meander pattern is to No meander pattern is to DEPTH (d BANKFULL MAX max), ft BANK HEIGHT RATIO dominated by agricultural fields with lateral drainage ditches. Remnant dominated by agricultural fields with lateral drainage ditches. Remnant dominated by agricultural fields with lateral drainage ditches. Remnant ' be constructed for zero order channel. Restoration of the be constructed for zero order channel. Restoration of the No meander pattern is to be constructed for zero order channel. Restoration of the TYPICAL BANK HEIGHT ABOVE BANKFULL channels or valleys have channels or valleys have channels or valleys have BD-5 s zero order valley di l i l i t floodplain's natural floodplain's natural floodplain's natural WIDTH Flood-Prone Area ?fia), ft been plowed over through been plowed over through been plowed over through sp ays var ous ow po n s where saturation and groundwater hydrology groundwater hydrology groundwater hydrology and ENTRENCHMENT (ER) years of agricultural practices essentially Y years of agricultural practices essentially filling p Y g years of agricultural practices essentially filling Y g overland flows have and surface water flows i t i t d and surface water flows i t i t d surface water flows (rain t i t d t t MEANDER LENGTH (Lm), ( ), ft , filling in all low points. , in all low points. , in all low points. caused depressions, (ra n even s) s expec e to create natural braided (ra n even s) s expec e to create natural braided even s) s expec e o crea e natural braided low points RATIO OF Lm TO Wb?t however, no discernable h l h f d t low points throughout the low points throughout the throughout the valley. RADIUS OF CURVATURE, ft c anne as orme o convey flow. valley. Proposed valley valley. Proposed valley Proposed valley width was RATIO OF Rc TO Wbkf width was determined i t f th width was determined i t f th determined using contours o th ll fl f ll i dit h BELT WIDTH, ft us ng con ours o e valley floor following ditch us ng con ours o e valley floor following ditch e va ey oor o ow ng c fill. MEANDER WIDTH RATIO fill. fill. SINUOSITY (K) VALLEY SLOPE, ft/ft 7003 0.001 0.001 0.002 0.003 0.001 0.001 AVERAGE SLOPE (S), ft/ft RIFFLE SLOPE, ft/ft RATIO OF RIFFLE SLOPE TO AVERAGE SLOPE POOL SLOPE, ft/ft RATIO OF POOL SLOPE TO AVERAGE SLOPE MAX POOL DEPTH, ft RATIO OF POOL DEPTH TO AVERAGE BANKFULL DEPTH POOL WIDTH, ft RATIO OF POOL WIDTH TO BANKFULL WIDTH POOL TO POOL SPACING, ft RATIO OF POOL TO POOL SPACING TO BANKFULL WIDTH Morphological Characteristics of Bachelors Delight: HM-1 and Reference Reach: Bachelors Delight: HM-1 County: Onslow County, INC Design by: CLS Checked by: RVS ITEM Existing Conditions Reference Reach Reference Reach Proposed Conditions Proposed Conditions LOCATION HM-1 BD-2 - Downstream of Soil Road BD-5 Zero Order Bachelors Delight: HM-1 Zero Order Channel Bachelors Delight: HM-1 Single Thread Channel STREAM TYPE G5 - E5 E5 Zero Order Zero Order E5 DRAINAGE AREA, Ac - SgMi 62 Ac- 0.10 S Mi 83 Ac- 0.13S Mi 19.84S Mi 0.03S Mi 22 Ac-0.04S Mi 83 Ac- 0.13S Mi BANKFULL DISCHARGE, cfs 2.2 cfs 1.0 cfs BD-5's remnant realtively 2.0 cfs BANKFULL X-SECTION AREA (Abkf), ftZ 2.20 ft 2 2.6 ftZ , undisturbed zero order Existing ditch/channel to b fill d t i ti d 6.3 ft2 BANKFULL MEAN VELOCITY, fps 1.01 fps 0.4 fps channel is indicative of a e e o ex s ng groun at low point of valley. 0.7 fps BANKFULL WIDTH (Wbkf), ft 2.9 ft 4.1 ft natural zero order stream. 6.0 ft VALLEY TOE OF SLOPE WIDTH NA NA 52.0 ft 30.0 ft NA BANKFULL MEAN DEPTH (dbkf), ft 0.75 ft 0.63 ft 0.57 ft WIDTH/DEPTH RATIO (Wbkddbkf) 3.9 6.5 No meander pattern is to 10.5 BANKFULL MAX DEPTH (dm_), ft 1.01 ft 0.88 ft be constructed for zero order channel 0.86 ft BANK HEIGHT RATIO 2.97 1.00 . Restoration of the 1.00 TYPICAL BANK HEIGHT ABOVE BANKFULL 3.00 ft 0.88 ft s zero order valley dis la s la s various low oints floodplain's natural 0.86 ft WIDTH Flood-Prone Area W ft ( ?a), 7.5 ft 50.0 ft p p y p where saturation and groundwater hydrology gro 30.00 ft ENTRENCHMENT RATIO (ER) 2.57 12.2 overland flows have and surface water flows i t i t d 5.0 MEANDER LENGTH (Lm), ft 12.6 - 12.6 ft caused depressions, n even s) s expec e (ra to create natural braided 18.0 - 60.0 ft RATIO OF Lm TO Wbkf Stream has been 3.1 - 3.1 however, no discernable h l h f d t low points throughout the 3.0 - 10.0 RADIUS OF CURVATURE, ft channelized and t i ht d th h th 2.0 - 4.4 ft c anne as orme o convey flow. valley. Proposed valle Y 12.0 - 18.0 ft RATIO OF Rc TO Wbkf s ra g ene roug e vall displaying no natural Y 0.5 - 1.1 width was determined i t f th 2.0 - 3.0 BELT WIDTH, ft . meander pattern. 9.6 - 9.6 ft us ng con ours o e valley floor following ditch 10.1 - 34.4 ft MEANDER WIDTH RATIO 2.3- 2.3 fill. 1.7 - 5.7 SINUOSITY (K) 1.02 1.25 1.26 VALLEY SLOPE, ft/ft 0.0039 ft/ft* 0.0027 ft/ft 0.002 ft/ft 0.0039 ft/ft 0.0039 ft/ft AVERAGE SLOPE (S), ft/ft 0.0069 ft/ft** 0.0024 ft/ft 0.0019 ft/ft RIFFLE SLOPE, ft/ft 0.0128 ft/ft 0.0136 ft/ft 0.0023 ft/ft RATIO OF RIFFLE SLOPE TO AVERAGE SLOPE 1.8 5.7 1.2 POOL SLOPE, ft/ft 0.0025 ft/ft 0.0010 ft/ft 0.0000 ft/ft RATIO OF POOL SLOPE TO AVERAGE SLOPE 0.4 0.4 0.0 MAX POOL DEPTH, ft 1.34 ft 1.26 ft 1.14 ft RATIO OF POOL DEPTH TO AVERAGE BANKFULL DEPTH 1.8 2.0 2.0 POOL WIDTH, ft 5.0 ft 7.18 ft 6.60 ft RATIO OF POOL WIDTH TO BANKFULL WIDTH 1.7 1.76 1.10 POOL TO POOL SPACING, ft 26.15 - 39.31 ft 3.3 -1 12.9 ft 6.0 - 30.0 ft RATIO OF POOL TO POOL SPACING TO BANKFULL WIDTH 8.96 - 13.46 0.8 J 3.2 1.0 - 5.0 * Valley Slope, and Sinuosity were taken from topographical data obtained on the entire site for existing conditions (i.e. data was not taken along reach lengths). ** Average Slope was taken along a reach length for existing conditions. APPENDIX F. HISTORIC AERIAL PHOTGRAPHY 2,N?'' fs ?'Fi4r ' 4 i?t? wd •` 11 ? Ik?t ?. r iF, 11 jl I FY'at: . ??. ?. ? .s v1f'F H iy ? f I Sa ti3 c A ' 1 fT?'a jF y V, Ma• r , r F y i7 *Boundaries are approximate and are not meant to be absolute. Map Source: 1938 Onslow County Aerial SCALE 1" =1600' ? ? ?t,x •1", rF!?,r(, 1F i. t ?e ? a r Jrhh4,•?? , t„ ?. t r - ?. • 7 7"?!t''! `?d? • ? t?.a `w?9+'u?" ti r - ? ? r%* i -tr,. ` {r !3+ a 4 ! * "'a1 "' +1 f T ''? xe?,+r??? ?v wy ?i?r.} 1 n t` >.? ( K ? - ? •, *? r n id..? t ° 1 4 e I r 1 i ? ': f! ? i' ? .•? h ? nom... ?^" t r.. ;4 .1 '„e? eZe ? r? . ' , .t,. r it ,e e- .++ ?f L y i ',•? it +• 1?k• r t.•, 5„ .F ? to :? '` t ?.` { ?{ , i ! : { ti ?. ?, is f ?,, "? t"vii i• { 6 1 ?1 'rr?r91 iyr 'r yYt )k° kkjr kiy i 4r1 rf 9 t t 't8y 1 4 w :t ? t , AF ?? I 1? 1 ! a? it ! 4 C r r?7 ??r r? r F3. a Y4 ^ j A,?i ?i • Fri a? i"" s ?r ^, .? «?it? '?,bt'd?? P ¢ ????„?? ?!i G f .? i { d ,? e. t ! 7 i ? ?' • ? .f . ' ? 4' =?''.? fY?p"v B ?'?aai ?'1 u ? a } M . 5? Lr P 'n ? r ? aR' r .L G (( 3+? . I " ? ? I Vli ?Y 5 ';irn? / .. ?? I I } r i 1•. A.?? tl.?t ?. , jP ' do f?N ^" '. y 8 li % ,F r. A + 4 r s4 r? y d ?. Ill T 4_I r • A ? z 2 a v a 1. i .. ?f l ?-r f 1 1. 3 ?' . r nV Q? r ?? ?;; I A F .) L, 4 :•f ? ? a?, r ` ;, - ,?,r. ?, ?1 ? S ':.nl?rr„ Y + t « 4, A ' ! rc? rrg c r `y s? n d2 r F' ..F r ??., r?lC ?1f\`Tn?I p? S? f ?t v 4a n ;lf K.• H.. Ip ?! f `' 1 day t k+,, IMP It? 7 ? jr-.a19 ra, . r •+aC r esJlf .,... A ?? r l[`.F .%'i t +4., ??? .?l ?ILL+- a: ?? 1f l ?! -? 9 ff f ?fi ? ?I j ?; _I' ? • , IJ ? .- .. i f ? tr y p'v' ? ;t iN. r8{ }i fi 1' .? it i' ( .iv ' 1 +° ", " If ••I /1':J. ! o C 1 y . ?. It .,p• fir' }r M. ?` rC i':,: n'? •i r•?,,fr, .r/ t' ,.f if 1 r 1 4 , r.2?' trt ( Y' { ',(} ',r rI *?: it ?, (( tln ! 4 '--.'r 'I•,. ;r `. ? 4 7n v t r. W'.' Yn r r r(?4 .3 1 , f r Y' (:. r ,r, jt t J / ryi}A? ??! 1 <t4 ii461 .n '1i z?° r ttt f.-?i?r/a ,YrA•f '"'?J, ?' - f` :nr7 .? 4a n +-•"e.'1. '>.w'f :tJ, i., r'r' '1!: }/?{f fY+ ld' d. •.jr, 'u,i' • N '4: a . r N f n {"' i,?r yJ .a` vl• q' rrr. IT 'f U r ',:? 1N a' P i br S4' n .?(.,Y .at' AJI, ?1 Y. ? ti '?. Ci ^Y "" W:;w d n ra.; ? a? r'w i.f i'° ? :-r ,•.r Y i. rj ^' n?' ? ? y r'f 1?.+? klF .,y r'.4 ? : Aa1k i P ,"" jY t ? i? . ,d .S' 4 w• lar 4 ;.Lt (1 S, r 1 ,? r ej?.f -',? r ? •.• X }? F ?F J.. C' f ?, j: a)•jfr L FT _.. '(%i ? i •a 1 .rYr? 'r r iF. :X a Ir rt . 1 •4? '?. d' r ?"• 1 ..i + .l'n. }t r c.4?? ,+' ^ fi i F'y P r •4 ' Wi• ?::? 1;'• ? !' t r? '' ?J ? ,i ?l 1} ? ? r1 ?? 1' 'r 1?Y ? ? Y,? {J ra 47 ;I "' 9"., "• d .r f +t ;'?' '?i:raY.,,? 4''! v .-c q"? '1%e i .i(. f fy},? y ,? ,?7i' 7 ? 'y • jV t?_ ? ? •"r? q,? ?.,?I>. t1? ? t N? ? tw4r? • F ?r '?'Y. ;f w r' ? r 4'1 r'? e• ? 1? +,.y•r t ?M. r?, '.', y at J?1?15.;1%.' I ?,. inF4#'ti !r # ? :. 11 'C.!?. t { ???.rc ?t ?2{f ?'' c'YR1? _" f?.,,t1. , ?{'4.w' a`+ ?%tf 4• ? ??.,`?yN""+ ?. "I";{''' ? #??'?*("?[( a'?.y 'I'?,." 41,fwu!. i F?flf?.?? "°?•'" ??r ' u9,4uvY?? , rF- '4f ?'?t? `•?f ??', r? 1•t{'r, - + V.. . ?.. ,I !... W. 4tf f AZk ?':.' .r. a. ??r?; t"?,?? t?1,:k- ?t,?"'?+l. i« ?" *° ...... .. ?` w All ?• ?`r f ? . N CY ? .b Fr .?3 ?..: 6rir#tv lt...?r ' .rs P? *Boundaries are approximate and are not meant to be absolute. Map Source: 1949 Onslow County Aerial SCALE 1" =1600' 1 >` 1 e J - s ? r r x u F ty yS,? rr?- ri?. r 1 ;X? ti G SQ A •'4 4y, I .56 HS I SA 1 } ! ?, air ? rhd, ? fP n ?t r r?'kt 1 ?yiy b G ??u M rr R? - Z0 d? " ` 1{t4- ?? ??''•? ( -, 4 ? , E A A ?Q f ? J Y ?1 b" ? r ! 1 ?_•fE l - f 1 tl1^ iili F + . >i??? ? Y ? r I J +s+ 1'?'t4 •'„?•?' P i?,'`.?c.', ? M- ,yv t ' -.} 18A 1, ?d t:'r ti',''?, ? ?' ` ?r? ?7vY``f .y r r ? ?`p;!w'F yJ?t4 ?? F r;'A'r. .w s V f s ?3 .' iar i r+ h,i '? ?'f u x 1 ci k ?. ??al+}". y I < ? Is .. l4? _ ? ? ,. r,?L ^??"yt ,,.n ' ??? •' - w ik +j?'?i njss???»k Bachelors Delight Mitigation Bank ?LMG Onslow County, NC *Boundaries are approximate and are 01-09-168 www not meant to be absolute. .LMGroup.net December 2009 Phone: 910.452.0001 -1.866.LMG.1078 Map Source: 1960 Onslow County Aerial Fax: 910.452.0060 P.O. Box 2522, Wilmington, NC 28402 1960 Aerial SCALE 1" =1600' • Y x? A.IK ? k r? ? y N-1 Ask ! 1 ' r r f ? k3;, 1 41 I?' y :'?;?'?•i •r r=' ..7.11 ,.? ? ? ? ? • ,: ., you ? F{ '4 .??*p • ?ti '7e Y ?Irr.. ?,yv,h J?. V ? ' i YI?JY / 'C `+ -1'•?c1 ?k i ?. ?. ? ? ?{'?,? ' ?_ f..'. .,?. `y Yid ?`!_ /. ,. ,•,?.L;._ 9 ` 4 •'? N *Boundaries are approximate and are not meant to be absolute. Map Source: 1970 Onslow County Aerial Bachelors Delight Mitigation Bank 1LMG Onslow County, NC 01-09-168 www.LMGroup.net 1970 Aerial December 2009 Phone: 910.452.0001 -1.866.LMG.1078 Fax: 910.452.0060 P.O. 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'.t F ?"-'?`?:._',"?r,?,• -:i+ _ _. ? ?j, ,,?,? s' .2 nr II ll F A ?-?' _ ? ? _ s LI, f ` ??, x? r/ - '-' 'I ?y,? ?,,i• '' Y .'{q pw fw ''id Bachelors Delight Mitigation Bank Onslow County, NC 1LMG *Boundaries are approximate and are 01-09-168 - www.LMGroup.net 2001 Aerial not meant to be absolute. December 2009 Phone: 910.452.0001 r1.866.LMG.1078 Map Source: 2001 Onslow County Aerial Fax: 910.452.0060 P.O. Box 2522, Wilmington, NC 28402 SCALE 1" -1600' APPENDIX G. STREAM BUFFER EFFECTIVENESS CORRECTION FACTOR (SBCF) MAPS i Wet Ford - -------------- --- ,s Wet Ford Fes` ` 10W -- - - - - - - - - - - - - --- - ---- Legend (NOTE: Acreage And Distances Provided Are For Complete Project) Property Boundary Reach HeWttts Branch (HE-1) Existing Roads Design Length 5,103 If - - - Stream Restoration (-9,679 If) Section ' North Side Average Buffer BCF Multiplier South Side Average Buffer BCF Multiplier Total Credits 1 (0-500 ) 400 1.13 262 1.13 565 2 (500'- 1.000) 267 1.13 199 1.13 565 'tea ,. v Stream Enhancement (^'5,928 If) 3 (1,000'- 1,500') 186 1.13 199 1.13 565 4(1,500-2,000') _ 306 1.13 1 161 1_ 1.13 565 Zero Order Restoration (7,082 If) 5 (2,000'- 2,500') 284 1.13 137 1.1 558 6 (2,500'- 3,000) 189 1.13 159 1.13 565 Stream Preservation (-11,400 If) 7 (3.000'-3,500') ' ' 197 1.13 198 1,13 565 8(3,506 -4,000 ) 197 1.13 197 1.13 565 9 (4,000 '- 4,500') 178 1.13 174 1 .13 565 Slreom 0erlan e parian Wetland Restoration (-60 ac.) Ri ` ------ 10 (4,500.5,000') 175 1.13 182 1.13 565 . Hutch son KolFlorenae L Hutcheson 11 (5,000'- 5,103) 160 1.13 192 1.13 116 ! 5121 Krgdom way, suite 100 Wetland Enhancement (-28 ac.) r' Ra1elgh, NC 29609 TOTAL 5,759 919-851-6x66 Riparian Wetland Preservation (-48 ac.) B P`°'e h l D li htS - ° Rev 1iao0 11 12010 9/1 /10 ? L?'?1G ac e ors e g wamp 5 6 Stream and Wetland Mitigation Bank Stream Buffer SBCF 35 ac. ?"? scale '°b"umber 1"=200' 01 09 168 Title: - - 0 50 100 200 400 Post Office Box 2522 HEA (Downstream) Drawn By: Sheet Number Upland Buffer (-94 ac.) Wilmington, North Carolina 28402 SBCF Sections1-6 CBM Figure 1 Telephone: 910-452-0001 . _:1WETLANDS@009 WETLANDS FILES101-09-168 -- Onslow 19 Batchelors, DowneylACADlOctober 20101AppG-SBCFLayouts-Oct2010.dwg M N 1 Wet Ford Legend (NOTE: Acreage And Distances Provided Are For Complete Project) Property Boundary Reach Hewitts Branch (HE-1) Existing Roads Design Length 5,10311 Stream Restoration (9,679 ID Section North Side Average Buffer BCF Multiplier south 1 (0-500') 400 1.13 Stream Enhancement (5 928 If) 2 (5°0.1.600') ' 267 1.13 , 3 (1,000 -1.500') 186 1.13 4 (1.500 -2.0( Zero Order Restoration (7,082 If) 5 (2000 -2.5( 6 (2500' - 3.0( Stream Preservation (-11,400 ID 7 (3,000'- 3-5( 8 (3,500' - 4.0( Riparian Wetland Restoration (-60 ac.) 9 (4.000' - 4,5( 10 (4,560.5,0 - 11 (5.000-- 5.1 Wetland Enhancement (-28 ac.) Riparian Wetland Preservation (-48 ac.) Stream Buffer (SBCF)(35 ac.) I? Upland Buffer (-94 ac.) .:1WETLANDS12009 WETLANDS FILES101-09-188 -- Onslow 19 Batchelots, Downey\ACADIOctober 2010tAppG-SBCFLayouts-01 60 1.13 ro ?J Side Average Buffer BCF Multiplier Total Credits 262 1.13 565 199 1.13 565 199 1.13 565 _ 161 1.13 565 137 1.1 558 159 1.13 565 198 1.13 565 197 1.13 565 174 1.13 565 Stream Design Provided by: 182 113 565 Ko/Flcrence L Hutcheson 192 1.13 116 5121 Kngdom Way, Suite loo Raleigh, NC 27607 919-851-6066 TOTAL 5,759 Project: Dale: Revision Date: LMG 4 1/5(20 10 Bachelors l an 9/15110 - and Wetl d Mitigation Bank Stream l ANnvasm:FMI11 cR'I P . Scale: Job Number: - -'..:.,, ..:,. r,,.,..^.e, 1..=200' 01-09-166 Title: 0 50 100 200 400 Post Office Box 2522 HEA(Upstream) Dmvm By Sheet Number Wilmington, North Carolina 28402 SBCF Sections 7-11 CBM Fi ure 2 Telephone: 910-452-0001 g . 1 1 1 11 1 1 1 1 11 11 1 1 1 1 1 1 1 1 1 1 wl 1 1 1 1 1 1 a?1 1 1 1 1 1 1 1 1 1 ! ?` 1 1 1, 11 1 1. 1. 1 11 1 ? 1 1 s? ?; ?? 11 1 1 1 1 1 `''° CC 1 1 , 1 1 1 1 1 1 L 1 ?1 1 1 1 1 1 1 1 1 1 1_. ?.Ot1 1 1 1 1 ,? 1 ; 1 1 1 1 1 1 1 1 11 1 1 1 1 1 1 1 , ? 1 1 1 1 1 1 1 1 1 11 1 1 1 1 1 1 1 1 • • ?. 1 .. . ... ...... Legend (NOTE: Acreage And Distances Provided Are For Com plete Project) 1 1 1 . Property Boundary Existing Roads Reach Huffm a ns Branch (HU-1) Stream Restoration (-9,679 If) Design (Length 3,445 If Stream Enhancement (5,928 If) Section East Side Average Buffer BCF Multiplier West Side Average Buffer BCF Multiplier Total Credits 1 (0 -172) 159 1.13 112 1.1 189 Zero Order Restoration (7,082 ID 2 (172'- 672) 179 1.13 183 1.13 565 3 (672'- 1. 172') 194 1.13 297 1.13 565 Stream Preservation (11,400 If) 1 4 (1,172 1.672) 180 1.13 300 1.13 565 5 (1,672'- 2,172) 166 1.13 225 1.13 558 Riparian Wetland Restoration (-60 ac.) ---------- 6 (2,172' 2,672') 167 1.13 177 1.13 565 7(2,672'-3,172) 171 1.13 162 1.13 565 Stream Design Provided by. IrTJT _ Wetland Enhancement (28 ac.) J 8 { 3,172'- 3,445') 173 1.13 124 1.1 304 Ke/fierenee S Hutcheson 5121 Kngdom Wag Salle 100 Raleigh, NC 27607 Riparian Wetland Preservation (-48 ac.) ® TOTAL 3,676 919-1551-6966 Project: Date: Revision Dale: LMG answamp vW2o,o Bachelors 9/15110 Stream (SBCF)( u?rNPxl I aNn p+e+? Stream and Wetland Mitigation Bank . Srele: Job Number Title: 1'=200' 01-09-166 Upland Buffer (-94 ac.) 0 50 100 200 400 Post Office Box 2522 HU-1SBCFSections l-8 Dram By: Sheet Number Wilmington, North Carolina 28402 CBM Figure 3 Telephone: 910-452-0001 . L:IWETLANDS12009 WETLANDS FILES101-09-188 -- Onslow 19 Batchelors, Downey\ACAD1October 20101AppG-SBCFLayouts-0d2010.dwg .f?`. ? - - Wet Ford Legend (NOTE: Acreage And Distances Provided Are For Complete Project) Property Boundary Existing Roads Stream Restoration (9,679 If) Stream Enhancement (-5,928 If) Zero Order Restoration (7,082 If) Reach Design Length Stream Preservation (-11,400 If) Section 1 (0-500.) Riparian Wetland Restoration (-60 ac.) Y 2 (500 -1,000") 3 {1,000' -1.131 Wetland Enhancement (-28 ac.) ' " Riparian Wetland Preservation (-48 ac.) Stream Buffer (SBCF)(-35 ac.) Upland Buffer (-94 ac.) _:1WETLANDS@009 WETLANDS FILES101-09-168 -- Onslow 19 Batchelors, DoxneylACADIOctober 20101AppG-SBCFLayouts-Oct201( Half Moon Swamp (HNC-1) 1,131 If East Side Average Buffer 227 183 160 _ -1 27 _ -ten, BCF Multiplier West Side Average Buffer BCF Multip 1.13 230 1.13 1.13 176 1.13 1.13 J 167 1.13 TOTAL 0 50 100 200 400 r Total Credits 565 565 148 1,278 LMG l 1 AI AnIiPost Office Box 2522 Wilmington, North Carolina 28402 Telephone: 910-452-0001 d: Dale. Bachelors Delight Swamp 1/512010 m and Wetland Mitigation Bank Boale: 1"= 200' HM-1 SBCF Sections 1-3 I Drawn By: CBM Stream Design Provke0 or. Ko/Florence 8 Hutcheson 5121 Kingdom Way, Suite 100 Raleigh, NC 27607 919851-6066 Revision Date: 9115/10 Job Number 01-09-168 Sheet Number Figure 4. APPENDIX H. NC WAM FIELD ASSESSMENT FORMS NC WAM FIELD ASSESSMENT FORM Accompanies User Manual Version 3.0 c:aicuiator version ;s.u Wetland Site Name Bachelor's Delight - BD7 Date 6/2/10 Wetland Type Bottomland Hardwood Forest Assessor Name/Organization CN,DB / LMG Level III Ecoregion Middle Atlantic Coastal Plain Nearest Named Water Body Bachelors Delight Swamp River Basin White Oak USGS 8-Digit Catalogue Unit 03030001 M Yes Fl No Precipitation within 48 hrs? Latitude/Lonaitude (deci-dearees) 34.85371 / -77.44935 Evidence of stressors affecting the assessment area (may not be within the assessment area) Please circle and/or make note below if evidence of stressors is apparent. Consider departure from reference, if appropriate, in recent past (for instance, within 10 years). Noteworthy stressors include, but are not limited to the following. • Hydrological modifications (examples: ditches, dams, beaver dams, dikes, berms, ponds, etc.) • Surface and sub-surface discharges into the wetland (examples: discharges containing obvious pollutants, presence of nearby septic tanks, underground storage tanks (USTs), hog lagoons, etc.) • Signs of vegetation stress (examples: vegetation mortality, insect damage, disease, storm damage, salt intrusion, etc.) • Habitat/plant community alteration (examples: mowing, clear-cutting, exotics, etc.) Is the assessment area intensively managed? ? Yes ® No Describe effects of stressors that are present. Regulatory Considerations Select all that apply to the assessment area. ? Anadromous fish ? Federally protected species or State endangered or threatened species ? NCDWQ riparian buffer rule in effect ? Abuts a Primary Nursery Area (PNA) ? Publicly owned property ? N.C. Division of Coastal Management Area of Environmental Concern (AEC) (including buffer) ? Abuts a stream with a NCDWQ classification of SA or supplemental classifications of HQW, ORW, or Trout ? Designated NCNHP reference community ® Abuts a 303(d)-listed stream or a tributary to a 303(d)-listed stream What type of natural stream is associated with the wetland, if any? (Check all that apply) ® Blackwater ? Brownwater ? Tidal (if tidal, check one of the following boxes) ? Lunar ? Wind ? Both Is the assessment area on a coastal island? ? Yes ® No Is the assessment area's surface water storage capacity or duration substantially altered by beaver? ? Yes ® No 1. Ground Surface Condition/Vegetation Condition -assessment area condition metric Check a box in each column. Consider alteration to the ground surface (GS) in the assessment area and vegetation structure (VS) in the assessment area. Compare to reference wetland if applicable (see User Manual). If a reference is not applicable, then rate the assessment area based on evidence an effect. GS VS ®A ®A Not severely altered ?B ?B Severely altered over a majority of the assessment area (ground surface alteration examples: vehicle tracks, excessive sedimentation, fire-plow lanes, skidder tracks, bedding, fill, soil compaction, obvious pollutants) (vegetation structure alteration examples: mechanical disturbance, herbicides, salt intrusion [where appropriate], exotic species, grazing, less diversity [if appropriate], artificial hydrologic alteration) Surface and Sub-Surface Storage Capacity and Duration - assessment area condition metric Check a box in each column. Consider surface storage capacity and duration (Surf) and sub-surface storage capacity and duration (Sub). Consider both increase and decrease in hydrology. Refer to the current NRCS lateral effect of ditching guidance for North Carolina hydric soils (see USACE Wilmington District website) for the zone of influence of ditches in hydric soils. A ditch <_ 1 foot deep is considered to affect surface water only, while a ditch > 1 foot deep is expected to affect both surface and sub-surface water. Consider tidal flooding regime, if applicable. Surf Sub ®A ®A Water storage capacity and duration are not altered. ?B ?B Water storage capacity or duration are altered, but not substantially (typically, not sufficient to change vegetation). ?C ?C Water storage capacity or duration are substantially altered (typically, alteration sufficient to result in vegetation change) (examples: draining, flooding, soil compaction, filling, excessive sedimentation, underground utility lines). Water Storage/Surface Relief- assessment area/wetland type condition metric Check a box in each column. Select the appropriate storage for the assessment area (AA) and the wetland type (WT). AA WT ?A ?A Majority of wetland with depressions able to pond water > 1 deep ®B ®B Majority of wetland with depressions able to pond water 6 inches to 1 foot deep ?C ?C Majority of wetland with depressions able to pond water 3 to 6 inches deep ?D ?D Depressions able to pond water < 3 inches deep ?A Evidence that maximum depth of inundation is greater than 2 feet ®B Evidence that maximum depth of inundation is between 1 and 2 feet ?C Evidence that maximum depth of inundation is less than 1 foot 4. Soil Texture/Structure - assessment area condition metric Check a box from each of the three soil property groups below. Dig soil profile in the dominant assessment area landscape feature. Make soil observations within the top 12 inches. Use most recent National Technical Committee for Hydric Soils guidance for regional indicators. ?A Sandy soil ®B Loamy or clayey soils exhibiting redoxymorphic features (concentrations, depletions, or rhizospheres) ?C Loamy or clayey soils not exhibiting redoxymorphic features ?D Loamy or clayey gleyed soil ?E Histosol or histic epipedon ?A Soil ribbon < 1 inch ®B Soil ribbon ? 1 inch ?A No peat or muck presence ®B A peat or muck presence 5. Discharge into Wetland - opportunity metric Check a box in each column. Consider surface pollutants or discharges (Surf) and sub-surface pollutants or discharges (Sub) Examples of sub-surface discharges include presence of nearby septic tank, underground storage tank (UST), etc. Surf Sub ®A ®A Little or no evidence of pollutants or discharges entering the assessment area ?B ?B Noticeable evidence of pollutants or discharges entering the wetland and stressing, but not overwhelming the treatment capacity of the assessment area ?C ?C Noticeable evidence of pollutants or discharges (pathogen, particulate, or soluble) entering the assessment area and potentially overwhelming the treatment capacity of the wetland (water discoloration, dead vegetation, excessive sedimentation, odor) Land Use - opportunity metric Check all that apply (at least one box in each column). Evaluation involves a GIS effort with field adjustment. Consider sources drainin g to assessment area within entire upstream watershed (WS), within 5 miles and within the watershed draining to the assessment area (5M), and within 2 mi les and within the watershed draining to the assessment area (2M). WS 5M 2M ?A ?A ?A > 10% impervious surfaces ®B ®B ?B < 10% impervious surfaces ?C ?C ?C Confined animal operations (or other local, concentrated source of pollutants ?D ?D ?D ? 20% coverage of pasture ?E ?E ®E ? 20% coverage of agricultural land (regularly plowed land) ?F ?F ?F ? 20% coverage of maintained grass/herb ?G ?G ?G ? 20% coverage of silvicultural land characterized by a clear-cut < 5 years old ?H ?H ?H Little or no opportunity to improve water quality. Lack of opportunity may result from hydrologic alterations that prevent drainage or overbank flow from affecting the assessment area. 7. Wetland Acting as Vegetated Buffer -assessment area condition metric 7a. Is assessment area within 50 feet of a tributary or other open water? ®Yes ?No If Yes, continue to 7b. If No, skip to Metric 8. Wetland buffer need only be present on one side of the water body. Make buffer judgment based on the average width of wetland. Record a note if a portion of the buffer has been removed or disturbed. 7b. How much of the first 50 feet from the bank is wetland? Descriptor E should be selected if ditches effectively bypass the buffer. ®A ? 50 feet ?B From 30 to < 50 feet ?C From 15 to < 30 feet ?D From 5 to < 15 feet ?E < 5 feet or buffer bypassed by ditches 7c. Tributary width. If the tributary is anastomosed, combine widths of channels/braids for a total width. ?<_ 15-feet wide ®> 15-feet wide ? Other open water (no tributary present) 7d. Do roots of assessment area vegetation extend into the bank of the tributary/open water? ®Yes ?No 7e. Is stream or other open water sheltered or exposed? ®Sheltered - adjacent open water with width < 2500 feet and no regular boat traffic. ? Exposed - adjacent open water with width ? 2500 feet or regular boat traffic. 8. Wetland Width at the Assessment Area -wetland type/wetland complex condition metric Check a box in each column for riverine wetlands only. Select the appropriate width for the wetland type at the assessment area (WT) and the wetland complex at the assessment area (WC). See User Manual for WT and WC boundaries. WT WC ®A ®A 100 feet ?B ?B From 80 to < 100 feet ?C ?C From 50 to < 80 feet ?D ?D From 40 to < 50 feet ?E ?E From 30 to < 40 feet ?F ?F From 15 to < 30 feet ?G ?G From 5 to < 15 feet ?H ?H < 5 feet 9. Inundation Duration - assessment area condition metric Answer for assessment area dominant landform. ?A Evidence of short-duration inundation (< 7 consecutive days) ?B Evidence of saturation, without evidence of inundation ®C Evidence of long-duration inundation or very long-duration inundation (7 to 30 consecutive days or more) 10. Indicators of Deposition - assessment area condition metric Consider recent deposition only (no plant growth since deposition). ®A Sediment deposition is not excessive, but at approximately natural levels. ?B Sediment deposition is excessive, but not overwhelming the wetland. ?C Sediment deposition is excessive and is overwhelming the wetland. 11. Wetland Size - wetland type/wetland complex condition metric Check a box in each column. Involves a GIS effort with field adjustment. This metric evaluates three aspects of the wetland area: the size of the wetland type (WT), the size of the wetland complex (WC), and the size of the forested wetland (FW) (if applicable, see User Manual). See the User Manual for boundaries of these evaluation areas. If assessment area is clear-cut, select "K" for the FW column. WT WC FW (if applicable) ?A ?A ®A ? 500 acres ?B ?B ?B From 100 to < 500 acres ®C ?C ?C From 50 to < 100 acres ?D ?D ?D From 25 to < 50 acres ?E ?E ?E From 10 to < 25 acres ?F ?F ?F From 5 to < 10 acres ?G ?G ?G From 1 to < 5 acres ?H ?H ?H From 0.5 to < 1 acre ?I ?I ?I From 0.1 to < 0.5 acre ?J ?J ?J From 0.01 to < 0.1 acre ?K ?K ?K < 0.01 acre or assessment area is clear-cut 12. Wetland Intactness - wetland type condition metric (evaluate for Pocosins only) ?A Pocosin is the full extent (? 90%) of its natural landscape size. ?B Pocosin type is < 90% of the full extent of its natural landscape size. 13. Connectivity to Other Natural Areas - landscape condition metric 13a. Check appropriate box(es) (a box may be checked in each column). Involves a GIS effort with field adjustment. This metric evaluates whether the wetland is well connected (Well) and/or loosely connected (Loosely) to the landscape patch, the contiguous naturally vegetated area and open water (if appropriate). Boundaries are formed by four-lane roads, urban landscapes, maintained fields (pasture and agriculture), or open water > 300 feet wide. Well Loosely ®A ?A ? 500 acres ?B ?B From 100 to < 500 acres ?C ?C From 50 to < 100 acres ?D ?D From 10 to < 50 acres ? E ? E < 10 acres ?F ?F Wetland type has a poor or no connection to other natural habitats 13b. Evaluate for marshes only. ?Yes ?No Wetland type has a surface hydrology connection to open waters/stream or tidal wetlands. 14. Edge Effect - wetland type condition metric May involve a GIS effort with field adjustment. Estimate distance from wetland type boundary to artificial edges. Artificial edges include permanent features such as fields, development, two-lane or larger roads (? 40 feet wide), utility line corridors wider than a two-lane road, and clear-cuts < 10 years old. Consider the eight main points of the compass. ®A No artificial edge within 150 feet in all directions ?B No artificial edge within 150 feet in four (4) to seven (7) directions ?C An artificial edge occurs within 150 feet in more than four (4) directions or assessment area is clear-cut 15. Vegetative Composition - assessment area condition metric (skip for all marshes and Pine Flat) ®A Vegetation is close to reference condition in species present and their proportions. Lower strata composed of appropriate species, with exotic plants absent or sparse within the assessment area. ?B Vegetation is different from reference condition in species diversity or proportions, but still largely composed of native species characteristic of the wetland type. This may include communities of weedy native species that develop after clearcutting or clearing. It also includes communities with exotics present, but not dominant, over a large portion of the expected strata. ?C Vegetation severely altered from reference in composition. Expected strata are unnaturally absent or dominated by exotic species or composed of planted stands of non-characteristic species or inappropriately composed of a single species. 16. Vegetative Diversity - assessment area condition metric (evaluate for Non-tidal Freshwater Marsh only) ?A Vegetation diversity is high and is composed primarily of native species (< 10% cover of exotics). ?B Vegetation diversity is low or has > 10% to 50% cover of exotics. ?C Vegetation is dominated by exotic species (> 50 % cover of exotics). 17. Vegetative Structure - assessment area/wetland type condition metric 17a. Is vegetation present? ®Yes ?No If Yes, continue to 17b. If No, skip to Metric 18. 17b. Evaluate percent coverage of vegetation for all marshes only. Skip to 17c for non-marsh wetlands. ?A ? 25% coverage of vegetation ?B < 25% coverage of vegetation 17c. Check a box in each column for each stratum. Evaluate this portion of the metric for non-marsh wetlands. Consider structure in airspace above the assessment area (AA) and the wetland type (WT) separately. AA WT ®A ®A Canopy closed, or nearly closed, with natural gaps associated with natural processes ?B ?B Canopy present, but opened more than natural gaps ?C ?C Canopy sparse or absent ®A ®A Dense mid-story/sapling layer ?B ?B Moderate density mid-story/sapling layer ?C ?C Mid-story/sapling layer sparse or absent ?A ?A Dense shrub layer ®B ®B Moderate density shrub layer ?C ?C Shrub layer sparse or absent ?A ?A Dense herb layer ®B ®B Moderate density herb layer ?C ?C Herb layer sparse or absent 18. Snags - wetland type condition metric ®A Large snags (more than one) are visible (> 12 inches DBH, or large relative to species present and landscape stability). ?B NotA 19. Diameter Class Distribution - wetland type condition metric ®A Majority of canopy trees have stems > 6 inches in diameter at breast height (DBH); many large trees (> 12 inches DBH) are present. ?B Majority of canopy trees have stems between 6 and 12 inches DBH, few are > 12 inch DBH. ?C Majority of canopy trees are < 6 inches DBH or no trees. 20. Large Woody Debris - wetland type condition metric Include both natural debris and man-placed natural debris. ®A Large logs (more than one) are visible (> 12 inches in diameter, or large relative to species present and landscape stability). ?B NotA 21. Vegetation/Open Water Dispersion - wetland type/open water condition metric (evaluate for Non-Tidal Freshwater Marsh only) 22. Hydrologic Connectivity- assessment area condition metric Evaluate for riverine wetlands only. Examples of activities that may severely alter hydrologic connectivity include intensive ditching, fill, sedimentation, channelization, diversion, man-made berms, beaver dams, and stream incision. ®A Overbank and overland flow are not severely altered in the assessment area. ?B Overbank flow is severely altered in the assessment area. ?C Overland flow is severely altered in the assessment area. ?D Both overbank and overland flow are severely altered in the assessment area. Notes Channel anastomosed. Dry conditions at time of observation. NC WAM Wetland Rating Sheet Accompanies User Manual Version 3.0 Rating Calculator Version 3.0 Wetland Site Name Bachelor's Delight - BD7 Date of Assessment 6/2/10 Wetland Type Bottomland Hardwood Forest Assessor Name/Organization CN,DB / LMG Presence of stressor affecting assessment area (Y/N) NO Notes on Field Assessment Form (Y/N) YES Presence of regulatory considerations (Y/N) YES Wetland is intensively managed (Y/N) NO Assessment area is located within 50 feet of a natural tributary or other open water (Y/N) YES Assessment area is substantially altered by beaver (Y/N) NO Sub-function Ratina Summar Function Sub-function Metrics Rating Hydrology Surface Storage and Retention Condition MEDIUM Sub-surface Storage and Retention Condition LOW Water Quality Pathogen Change Condition LOW Condition/Opportunity LOW Opportunity Presence (Y/N) NO Particulate Change Condition HIGH Condition/Opportunity HIGH Opportunity Presence (Y/N) NO Soluble Change Condition HIGH Condition/Opportunity HIGH Opportunity Presence (Y/N) NO Physical Change Condition HIGH Condition/Opportunity HIGH Opportunity Presence (Y/N) NO Pollution Change Condition NA Condition/Opportunity NA Opportunity Presence (Y/N) NA Habitat Physical Structure Condition HIGH Landscape Patch Structure Condition HIGH Veqetation Composition Condition HIGH Function Ratina Summar Function Metrics Rating Hydrology Condition MEDIUM Water Quality Condition HIGH Condition/Opportunity HIGH Opportunity Presence (Y/N) NO Habitat Condition HIGH Overall Wetland Rating HIGH NC WAM FIELD ASSESSMENT FORM Accompanies User Manual Version 3.0 c:aicuiator version ;s.u Wetland Site Name BDMB - NCSU Block Date 6/2/10 Wetland Type Pine Flat Assessor Name/Organization CN,DB - LMG Level III Ecoregion Middle Atlantic Coastal Plain Nearest Named Water Body Huff mans Branch River Basin White Oak USGS 8-Digit Catalogue Unit 03030001 M Yes Fl No Precipitation within 48 hrs? Latitude/Lonaitude (deci-dearees) 34.86681 / -77.45574 Evidence of stressors affecting the assessment area (may not be within the assessment area) Please circle and/or make note below if evidence of stressors is apparent. Consider departure from reference, if appropriate, in recent past (for instance, within 10 years). Noteworthy stressors include, but are not limited to the following. • Hydrological modifications (examples: ditches, dams, beaver dams, dikes, berms, ponds, etc.) • Surface and sub-surface discharges into the wetland (examples: discharges containing obvious pollutants, presence of nearby septic tanks, underground storage tanks (USTs), hog lagoons, etc.) • Signs of vegetation stress (examples: vegetation mortality, insect damage, disease, storm damage, salt intrusion, etc.) • Habitat/plant community alteration (examples: mowing, clear-cutting, exotics, etc.) Is the assessment area intensively managed? ? Yes ® No Describe effects of stressors that are present. Roadside ditches may be affecting hydrology near the roads (outside edges of forest block). Bedding for silviculture has altered the ground surface but not severely. Regulatory Considerations Select all that apply to the assessment area. ? Anadromous fish ? Federally protected species or State endangered or threatened species ? NCDWQ riparian buffer rule in effect ? Abuts a Primary Nursery Area (PNA) ? Publicly owned property ? N.C. Division of Coastal Management Area of Environmental Concern (AEC) (including buffer) ? Abuts a stream with a NCDWQ classification of SA or supplemental classifications of HQW, ORW, or Trout ? Designated NCNHP reference community ? Abuts a 303(d)-listed stream or a tributary to a 303(d)-listed stream What type of natural stream is associated with the wetland, if any? (Check all that apply) ? Blackwater ? Brownwater ? Tidal (if tidal, check one of the following boxes) ? Lunar ? Wind ? Both Is the assessment area on a coastal island? ? Yes ® No Is the assessment area's surface water storage capacity or duration substantially altered by beaver? ? Yes ® No 1. Ground Surface Condition/Vegetation Condition -assessment area condition metric Check a box in each column. Consider alteration to the ground surface (GS) in the assessment area and vegetation structure (VS) in the assessment area. Compare to reference wetland if applicable (see User Manual). If a reference is not applicable, then rate the assessment area based on evidence an effect. GS VS ®A ®A Not severely altered ?B ?B Severely altered over a majority of the assessment area (ground surface alteration examples: vehicle tracks, excessive sedimentation, fire-plow lanes, skidder tracks, bedding, fill, soil compaction, obvious pollutants) (vegetation structure alteration examples: mechanical disturbance, herbicides, salt intrusion [where appropriate], exotic species, grazing, less diversity [if appropriate], artificial hydrologic alteration) Surface and Sub-Surface Storage Capacity and Duration - assessment area condition metric Check a box in each column. Consider surface storage capacity and duration (Surf) and sub-surface storage capacity and duration (Sub). Consider both increase and decrease in hydrology. Refer to the current NRCS lateral effect of ditching guidance for North Carolina hydric soils (see USACE Wilmington District website) for the zone of influence of ditches in hydric soils. A ditch <_ 1 foot deep is considered to affect surface water only, while a ditch > 1 foot deep is expected to affect both surface and sub-surface water. Consider tidal flooding regime, if applicable. Surf Sub ®A ?A Water storage capacity and duration are not altered. ?B ®B Water storage capacity or duration are altered, but not substantially (typically, not sufficient to change vegetation). ?C ?C Water storage capacity or duration are substantially altered (typically, alteration sufficient to result in vegetation change) (examples: draining, flooding, soil compaction, filling, excessive sedimentation, underground utility lines). Water Storage/Surface Relief- assessment area/wetland type condition metric Check a box in each column. Select the appropriate storage for the assessment area (AA) and the wetland type (WT). AA WT ?A ?A Majority of wetland with depressions able to pond water > 1 deep ?B ?B Majority of wetland with depressions able to pond water 6 inches to 1 foot deep ®C ®C Majority of wetland with depressions able to pond water 3 to 6 inches deep ?D ?D Depressions able to pond water < 3 inches deep ?A Evidence that maximum depth of inundation is greater than 2 feet ?B Evidence that maximum depth of inundation is between 1 and 2 feet ®C Evidence that maximum depth of inundation is less than 1 foot 4. Soil Texture/Structure - assessment area condition metric Check a box from each of the three soil property groups below. Dig soil profile in the dominant assessment area landscape feature. Make soil observations within the top 12 inches. Use most recent National Technical Committee for Hydric Soils guidance for regional indicators. ®A Sandy soil ?B Loamy or clayey soils exhibiting redoxymorphic features (concentrations, depletions, or rhizospheres) ?C Loamy or clayey soils not exhibiting redoxymorphic features ?D Loamy or clayey gleyed soil ?E Histosol or histic epipedon ®A Soil ribbon < 1 inch ?B Soil ribbon ? 1 inch ®A No peat or muck presence ?B A peat or muck presence 5. Discharge into Wetland - opportunity metric Check a box in each column. Consider surface pollutants or discharges (Surf) and sub-surface pollutants or discharges (Sub) Examples of sub-surface discharges include presence of nearby septic tank, underground storage tank (UST), etc. Surf Sub ®A ®A Little or no evidence of pollutants or discharges entering the assessment area ?B ?B Noticeable evidence of pollutants or discharges entering the wetland and stressing, but not overwhelming the treatment capacity of the assessment area ?C ?C Noticeable evidence of pollutants or discharges (pathogen, particulate, or soluble) entering the assessment area and potentially overwhelming the treatment capacity of the wetland (water discoloration, dead vegetation, excessive sedimentation, odor) Land Use - opportunity metric Check all that apply (at least one box in each column). Evaluation involves a GIS effort with field adjustment. Consider sources drainin g to assessment area within entire upstream watershed (WS), within 5 miles and within the watershed draining to the assessment area (5M), and within 2 mi les and within the watershed draining to the assessment area (2M). WS 5M 2M ?A ?A ?A > 10% impervious surfaces ®B ®B ®B < 10% impervious surfaces ?C ?C ?C Confined animal operations (or other local, concentrated source of pollutants ?D ?D ?D ? 20% coverage of pasture ?E ?E ?E ? 20% coverage of agricultural land (regularly plowed land) ?F ?F ?F ? 20% coverage of maintained grass/herb ?G ?G ?G ? 20% coverage of silvicultural land characterized by a clear-cut < 5 years old ?H ?H ?H Little or no opportunity to improve water quality. Lack of opportunity may result from hydrologic alterations that prevent drainage or overbank flow from affecting the assessment area. 7. Wetland Acting as Vegetated Buffer -assessment area condition metric 7a. Is assessment area within 50 feet of a tributary or other open water? ?Yes ®No If Yes, continue to 7b. If No, skip to Metric 8. Wetland buffer need only be present on one side of the water body. Make buffer judgment based on the average width of wetland. Record a note if a portion of the buffer has been removed or disturbed. 7b. How much of the first 50 feet from the bank is wetland? Descriptor E should be selected if ditches effectively bypass the buffer. ?A ? 50 feet ?B From 30 to < 50 feet ?C From 15 to < 30 feet ?D From 5 to < 15 feet ?E < 5 feet or buffer bypassed by ditches 7c. Tributary width. If the tributary is anastomosed, combine widths of channels/braids for a total width. ?<_ 15-feet wide ?> 15-feet wide ? Other open water (no tributary present) 7d. Do roots of assessment area vegetation extend into the bank of the tributary/open water? ?Yes ?No 7e. Is stream or other open water sheltered or exposed? ?Sheltered - adjacent open water with width < 2500 feet and no regular boat traffic. ? Exposed - adjacent open water with width ? 2500 feet or regular boat traffic. 8. Wetland Width at the Assessment Area -wetland type/wetland complex condition metric Check a box in each column for riverine wetlands only. Select the appropriate width for the wetland type at the assessment area (WT) and the wetland complex at the assessment area (WC). See User Manual for WT and WC boundaries. WT WC ®A ®A 100 feet ?B ?B From 80 to < 100 feet ?C ?C From 50 to < 80 feet ?D ?D From 40 to < 50 feet ?E ?E From 30 to < 40 feet ?F ?F From 15 to < 30 feet ?G ?G From 5 to < 15 feet ?H ?H < 5 feet 9. Inundation Duration - assessment area condition metric Answer for assessment area dominant landform. ®A Evidence of short-duration inundation (< 7 consecutive days) ?B Evidence of saturation, without evidence of inundation ?C Evidence of long-duration inundation or very long-duration inundation (7 to 30 consecutive days or more) 10. Indicators of Deposition - assessment area condition metric Consider recent deposition only (no plant growth since deposition). ®A Sediment deposition is not excessive, but at approximately natural levels. ?B Sediment deposition is excessive, but not overwhelming the wetland. ?C Sediment deposition is excessive and is overwhelming the wetland. 11. Wetland Size - wetland type/wetland complex condition metric Check a box in each column. Involves a GIS effort with field adjustment. This metric evaluates three aspects of the wetland area: the size of the wetland type (WT), the size of the wetland complex (WC), and the size of the forested wetland (FW) (if applicable, see User Manual). See the User Manual for boundaries of these evaluation areas. If assessment area is clear-cut, select "K" for the FW column. WT WC FW (if applicable) ?A ?A ®A ? 500 acres ®B ?B ?B From 100 to < 500 acres ?C ?C ?C From 50 to < 100 acres ?D ?D ?D From 25 to < 50 acres ?E ?E ?E From 10 to < 25 acres ?F ?F ?F From 5 to < 10 acres ?G ?G ?G From 1 to < 5 acres ?H ?H ?H From 0.5 to < 1 acre ?I ?I ?I From 0.1 to < 0.5 acre ?J ?J ?J From 0.01 to < 0.1 acre ?K ?K ?K < 0.01 acre or assessment area is clear-cut 12. Wetland Intactness - wetland type condition metric (evaluate for Pocosins only) ?A Pocosin is the full extent (? 90%) of its natural landscape size. ?B Pocosin type is < 90% of the full extent of its natural landscape size. 13. Connectivity to Other Natural Areas - landscape condition metric 13a. Check appropriate box(es) (a box may be checked in each column). Involves a GIS effort with field adjustment. This metric evaluates whether the wetland is well connected (Well) and/or loosely connected (Loosely) to the landscape patch, the contiguous naturally vegetated area and open water (if appropriate). Boundaries are formed by four-lane roads, urban landscapes, maintained fields (pasture and agriculture), or open water > 300 feet wide. Well Loosely ®A ?A ? 500 acres ?B ?B From 100 to < 500 acres ?C ?C From 50 to < 100 acres ?D ?D From 10 to < 50 acres ? E ? E < 10 acres ?F ?F Wetland type has a poor or no connection to other natural habitats 13b. Evaluate for marshes only. ?Yes ?No Wetland type has a surface hydrology connection to open waters/stream or tidal wetlands. 14. Edge Effect - wetland type condition metric May involve a GIS effort with field adjustment. Estimate distance from wetland type boundary to artificial edges. Artificial edges include permanent features such as fields, development, two-lane or larger roads (? 40 feet wide), utility line corridors wider than a two-lane road, and clear-cuts < 10 years old. Consider the eight main points of the compass. ®A No artificial edge within 150 feet in all directions ?B No artificial edge within 150 feet in four (4) to seven (7) directions ?C An artificial edge occurs within 150 feet in more than four (4) directions or assessment area is clear-cut 15. Vegetative Composition - assessment area condition metric (skip for all marshes and Pine Flat) ?A Vegetation is close to reference condition in species present and their proportions. Lower strata composed of appropriate species, with exotic plants absent or sparse within the assessment area. ?B Vegetation is different from reference condition in species diversity or proportions, but still largely composed of native species characteristic of the wetland type. This may include communities of weedy native species that develop after clearcutting or clearing. It also includes communities with exotics present, but not dominant, over a large portion of the expected strata. ?C Vegetation severely altered from reference in composition. Expected strata are unnaturally absent or dominated by exotic species or composed of planted stands of non-characteristic species or inappropriately composed of a single species. 16. Vegetative Diversity - assessment area condition metric (evaluate for Non-tidal Freshwater Marsh only) ?A Vegetation diversity is high and is composed primarily of native species (< 10% cover of exotics). ?B Vegetation diversity is low or has > 10% to 50% cover of exotics. ?C Vegetation is dominated by exotic species (> 50 % cover of exotics). 17. Vegetative Structure - assessment area/wetland type condition metric 17a. Is vegetation present? ®Yes ?No If Yes, continue to 17b. If No, skip to Metric 18. 17b. Evaluate percent coverage of vegetation for all marshes only. Skip to 17c for non-marsh wetlands. ?A ? 25% coverage of vegetation ?B < 25% coverage of vegetation 17c. Check a box in each column for each stratum. Evaluate this portion of the metric for non-marsh wetlands. Consider structure in airspace above the assessment area (AA) and the wetland type (WT) separately. AA WT ?A ?A Canopy closed, or nearly closed, with natural gaps associated with natural processes ?B ?B Canopy present, but opened more than natural gaps ®C ®C Canopy sparse or absent ?A ?A Dense mid-story/sapling layer ®B ®B Moderate density mid-story/sapling layer ?C ?C Mid-story/sapling layer sparse or absent ®A ®A Dense shrub layer ?B ?B Moderate density shrub layer ?C ?C Shrub layer sparse or absent ?A ?A Dense herb layer ®B ®B Moderate density herb layer ?C ?C Herb layer sparse or absent 18. Snags - wetland type condition metric ?A Large snags (more than one) are visible (> 12 inches DBH, or large relative to species present and landscape stability). ®B NotA 19. Diameter Class Distribution - wetland type condition metric ?A Majority of canopy trees have stems > 6 inches in diameter at breast height (DBH); many large trees (> 12 inches DBH) are present. ?B Majority of canopy trees have stems between 6 and 12 inches DBH, few are > 12 inch DBH. ®C Majority of canopy trees are < 6 inches DBH or no trees. 20. Large Woody Debris - wetland type condition metric Include both natural debris and man-placed natural debris. ?A Large logs (more than one) are visible (> 12 inches in diameter, or large relative to species present and landscape stability). ®B NotA 21. Vegetation/Open Water Dispersion - wetland type/open water condition metric (evaluate for Non-Tidal Freshwater Marsh only) 22. Hydrologic Connectivity- assessment area condition metric Evaluate for riverine wetlands only. Examples of activities that may severely alter hydrologic connectivity include intensive ditching, fill, sedimentation, channelization, diversion, man-made berms, beaver dams, and stream incision. ?A Overbank and overland flow are not severely altered in the assessment area. ?B Overbank flow is severely altered in the assessment area. ?C Overland flow is severely altered in the assessment area. ?D Both overbank and overland flow are severely altered in the assessment area. Notes Dry conditions at time of observation. NC WAM Wetland Rating Sheet Accompanies User Manual Version 3.0 Rating Calculator Version 3.0 Wetland Site Name Wetland Type BDMB - NCSU Block Date of Assessment 6/2/10 Pine Flat Assessor Name/Organization CN,DB - LMG Presence of stressor affecting assessment area (Y/N) YES Notes on Field Assessment Form (Y/N) YES Presence of regulatory considerations (Y/N) NO Wetland is intensively managed (Y/N) NO Assessment area is located within 50 feet of a natural tributary or other open water (Y/N) NO Assessment area is substantially altered by beaver (Y/N) NO Sub-function Ratina Summar Function Sub-function Metrics Rating Hydrology Surface Storage and Retention Condition HIGH Sub-surface Storage and Retention Condition MEDIUM Water Quality Pathogen Change Condition NA Condition/Opportunity NA Opportunity Presence (Y/N) NA Particulate Change Condition NA Condition/Opportunity NA Opportunity Presence (Y/N) NA Soluble Change Condition NA Condition/Opportunity NA Opportunity Presence (Y/N) NA Physical Change Condition NA Condition/Opportunity NA Opportunity Presence (Y/N) NA Pollution Change Condition HIGH Condition/Opportunity HIGH Opportunity Presence (Y/N) NO Habitat Physical Structure Condition LOW Landscape Patch Structure Condition HIGH Veqetation Composition Condition NA Function Ratina Summar Function Metrics Rating Hydrology Condition HIGH Water Quality Condition HIGH Condition/Opportunity HIGH Opportunity Presence (Y/N) NO Habitat Condition MEDIUM Overall Wetland Rating HIGH NC WAM FIELD ASSESSMENT FORM Accompanies User Manual Version 3.0 c:aicuiator version ;s.u Wetland Site Name BDMB- HU1A- Zero Order Date 6/2/10 Wetland Type Headwater Forest Assessor Name/Organization Corey Novak - LMG Level III Ecoregion Middle Atlantic Coastal Plain Nearest Named Water Body Huff mans Branch River Basin White Oak USGS 8-Digit Catalogue Unit 03030001 M Yes Fl No Precipitation within 48 hrs? Latitude/Lonaitude (deci-dearees) 34.86371 / -77.45233 Evidence of stressors affecting the assessment area (may not be within the assessment area) Please circle and/or make note below if evidence of stressors is apparent. Consider departure from reference, if appropriate, in recent past (for instance, within 10 years). Noteworthy stressors include, but are not limited to the following. • Hydrological modifications (examples: ditches, dams, beaver dams, dikes, berms, ponds, etc.) • Surface and sub-surface discharges into the wetland (examples: discharges containing obvious pollutants, presence of nearby septic tanks, underground storage tanks (USTs), hog lagoons, etc.) • Signs of vegetation stress (examples: vegetation mortality, insect damage, disease, storm damage, salt intrusion, etc.) • Habitat/plant community alteration (examples: mowing, clear-cutting, exotics, etc.) Is the assessment area intensively managed? ? Yes ® No Describe effects of stressors that are present. Roadside ditches may be affecting hydrology near road. Regulatory Considerations Select all that apply to the assessment area. ? Anadromous fish ? Federally protected species or State endangered or threatened species ? NCDWQ riparian buffer rule in effect ? Abuts a Primary Nursery Area (PNA) ? Publicly owned property ? N.C. Division of Coastal Management Area of Environmental Concern (AEC) (including buffer) ? Abuts a stream with a NCDWQ classification of SA or supplemental classifications of HQW, ORW, or Trout ? Designated NCNHP reference community ® Abuts a 303(d)-listed stream or a tributary to a 303(d)-listed stream What type of natural stream is associated with the wetland, if any? (Check all that apply) ® Blackwater ? Brownwater ? Tidal (if tidal, check one of the following boxes) ? Lunar ? Wind ? Both Is the assessment area on a coastal island? ? Yes ® No Is the assessment area's surface water storage capacity or duration substantially altered by beaver? ? Yes ® No 1. Ground Surface Condition/Vegetation Condition -assessment area condition metric Check a box in each column. Consider alteration to the ground surface (GS) in the assessment area and vegetation structure (VS) in the assessment area. Compare to reference wetland if applicable (see User Manual). If a reference is not applicable, then rate the assessment area based on evidence an effect. GS VS ®A ®A Not severely altered ?B ?B Severely altered over a majority of the assessment area (ground surface alteration examples: vehicle tracks, excessive sedimentation, fire-plow lanes, skidder tracks, bedding, fill, soil compaction, obvious pollutants) (vegetation structure alteration examples: mechanical disturbance, herbicides, salt intrusion [where appropriate], exotic species, grazing, less diversity [if appropriate], artificial hydrologic alteration) Surface and Sub-Surface Storage Capacity and Duration - assessment area condition metric Check a box in each column. Consider surface storage capacity and duration (Surf) and sub-surface storage capacity and duration (Sub). Consider both increase and decrease in hydrology. Refer to the current NRCS lateral effect of ditching guidance for North Carolina hydric soils (see USACE Wilmington District website) for the zone of influence of ditches in hydric soils. A ditch <_ 1 foot deep is considered to affect surface water only, while a ditch > 1 foot deep is expected to affect both surface and sub-surface water. Consider tidal flooding regime, if applicable. Surf Sub ?A ?A Water storage capacity and duration are not altered. ®B ®B Water storage capacity or duration are altered, but not substantially (typically, not sufficient to change vegetation). ?C ?C Water storage capacity or duration are substantially altered (typically, alteration sufficient to result in vegetation change) (examples: draining, flooding, soil compaction, filling, excessive sedimentation, underground utility lines). Water Storage/Surface Relief- assessment area/wetland type condition metric Check a box in each column. Select the appropriate storage for the assessment area (AA) and the wetland type (WT). AA WT ?A ?A Majority of wetland with depressions able to pond water > 1 deep ®B ®B Majority of wetland with depressions able to pond water 6 inches to 1 foot deep ?C ?C Majority of wetland with depressions able to pond water 3 to 6 inches deep ?D ?D Depressions able to pond water < 3 inches deep ?A Evidence that maximum depth of inundation is greater than 2 feet ?B Evidence that maximum depth of inundation is between 1 and 2 feet ®C Evidence that maximum depth of inundation is less than 1 foot 4. Soil Texture/Structure - assessment area condition metric Check a box from each of the three soil property groups below. Dig soil profile in the dominant assessment area landscape feature. Make soil observations within the top 12 inches. Use most recent National Technical Committee for Hydric Soils guidance for regional indicators. ?A Sandy soil ?B Loamy or clayey soils exhibiting redoxymorphic features (concentrations, depletions, or rhizospheres) ®C Loamy or clayey soils not exhibiting redoxymorphic features ?D Loamy or clayey gleyed soil ?E Histosol or histic epipedon ?A Soil ribbon < 1 inch ®B Soil ribbon ? 1 inch ®A No peat or muck presence ?B A peat or muck presence 5. Discharge into Wetland - opportunity metric Check a box in each column. Consider surface pollutants or discharges (Surf) and sub-surface pollutants or discharges (Sub) Examples of sub-surface discharges include presence of nearby septic tank, underground storage tank (UST), etc. Surf Sub ®A ®A Little or no evidence of pollutants or discharges entering the assessment area ?B ?B Noticeable evidence of pollutants or discharges entering the wetland and stressing, but not overwhelming the treatment capacity of the assessment area ?C ?C Noticeable evidence of pollutants or discharges (pathogen, particulate, or soluble) entering the assessment area and potentially overwhelming the treatment capacity of the wetland (water discoloration, dead vegetation, excessive sedimentation, odor) Land Use - opportunity metric Check all that apply (at least one box in each column). Evaluation involves a GIS effort with field adjustment. Consider sources drainin g to assessment area within entire upstream watershed (WS), within 5 miles and within the watershed draining to the assessment area (5M), and within 2 mi les and within the watershed draining to the assessment area (2M). WS 5M 2M ?A ?A ?A > 10% impervious surfaces ®B ®B ®B < 10% impervious surfaces ?C ?C ?C Confined animal operations (or other local, concentrated source of pollutants ?D ?D ?D ? 20% coverage of pasture ?E ?E ?E ? 20% coverage of agricultural land (regularly plowed land) ?F ?F ?F ? 20% coverage of maintained grass/herb ?G ?G ?G ? 20% coverage of silvicultural land characterized by a clear-cut < 5 years old ?H ?H ?H Little or no opportunity to improve water quality. Lack of opportunity may result from hydrologic alterations that prevent drainage or overbank flow from affecting the assessment area. 7. Wetland Acting as Vegetated Buffer -assessment area condition metric 7a. Is assessment area within 50 feet of a tributary or other open water? ?Yes ®No If Yes, continue to 7b. If No, skip to Metric 8. Wetland buffer need only be present on one side of the water body. Make buffer judgment based on the average width of wetland. Record a note if a portion of the buffer has been removed or disturbed. 7b. How much of the first 50 feet from the bank is wetland? Descriptor E should be selected if ditches effectively bypass the buffer. ?A ? 50 feet ?B From 30 to < 50 feet ?C From 15 to < 30 feet ?D From 5 to < 15 feet ?E < 5 feet or buffer bypassed by ditches 7c. Tributary width. If the tributary is anastomosed, combine widths of channels/braids for a total width. ?<_ 15-feet wide ?> 15-feet wide ? Other open water (no tributary present) 7d. Do roots of assessment area vegetation extend into the bank of the tributary/open water? ?Yes ?No 7e. Is stream or other open water sheltered or exposed? ?Sheltered - adjacent open water with width < 2500 feet and no regular boat traffic. ? Exposed - adjacent open water with width ? 2500 feet or regular boat traffic. 8. Wetland Width at the Assessment Area -wetland type/wetland complex condition metric Check a box in each column for riverine wetlands only. Select the appropriate width for the wetland type at the assessment area (WT) and the wetland complex at the assessment area (WC). See User Manual for WT and WC boundaries. WT WC ®A ®A 100 feet ?B ?B From 80 to < 100 feet ?C ?C From 50 to < 80 feet ?D ?D From 40 to < 50 feet ?E ?E From 30 to < 40 feet ?F ?F From 15 to < 30 feet ?G ?G From 5 to < 15 feet ?H ?H < 5 feet 9. Inundation Duration - assessment area condition metric Answer for assessment area dominant landform. ®A Evidence of short-duration inundation (< 7 consecutive days) ?B Evidence of saturation, without evidence of inundation ?C Evidence of long-duration inundation or very long-duration inundation (7 to 30 consecutive days or more) 10. Indicators of Deposition - assessment area condition metric Consider recent deposition only (no plant growth since deposition). ®A Sediment deposition is not excessive, but at approximately natural levels. ?B Sediment deposition is excessive, but not overwhelming the wetland. ?C Sediment deposition is excessive and is overwhelming the wetland. 11. Wetland Size - wetland type/wetland complex condition metric Check a box in each column. Involves a GIS effort with field adjustment. This metric evaluates three aspects of the wetland area: the size of the wetland type (WT), the size of the wetland complex (WC), and the size of the forested wetland (FW) (if applicable, see User Manual). See the User Manual for boundaries of these evaluation areas. If assessment area is clear-cut, select "K" for the FW column. WT WC FW (if applicable) ?A ?A ®A ? 500 acres ?B ?B ?B From 100 to < 500 acres ?C ?C ?C From 50 to < 100 acres ?D ?D ?D From 25 to < 50 acres ?E ?E ?E From 10 to < 25 acres ®F ?F ?F From 5 to < 10 acres ?G ?G ?G From 1 to < 5 acres ?H ?H ?H From 0.5 to < 1 acre ?I ?I ?I From 0.1 to < 0.5 acre ?J ?J ?J From 0.01 to < 0.1 acre ?K ?K ?K < 0.01 acre or assessment area is clear-cut 12. Wetland Intactness - wetland type condition metric (evaluate for Pocosins only) ?A Pocosin is the full extent (? 90%) of its natural landscape size. ?B Pocosin type is < 90% of the full extent of its natural landscape size. 13. Connectivity to Other Natural Areas - landscape condition metric 13a. Check appropriate box(es) (a box may be checked in each column). Involves a GIS effort with field adjustment. This metric evaluates whether the wetland is well connected (Well) and/or loosely connected (Loosely) to the landscape patch, the contiguous naturally vegetated area and open water (if appropriate). Boundaries are formed by four-lane roads, urban landscapes, maintained fields (pasture and agriculture), or open water > 300 feet wide. Well Loosely ®A ?A ? 500 acres ?B ?B From 100 to < 500 acres ?C ?C From 50 to < 100 acres ?D ?D From 10 to < 50 acres ? E ? E < 10 acres ?F ?F Wetland type has a poor or no connection to other natural habitats 13b. Evaluate for marshes only. ?Yes ?No Wetland type has a surface hydrology connection to open waters/stream or tidal wetlands. 14. Edge Effect - wetland type condition metric May involve a GIS effort with field adjustment. Estimate distance from wetland type boundary to artificial edges. Artificial edges include permanent features such as fields, development, two-lane or larger roads (? 40 feet wide), utility line corridors wider than a two-lane road, and clear-cuts < 10 years old. Consider the eight main points of the compass. ®A No artificial edge within 150 feet in all directions ?B No artificial edge within 150 feet in four (4) to seven (7) directions ?C An artificial edge occurs within 150 feet in more than four (4) directions or assessment area is clear-cut 15. Vegetative Composition - assessment area condition metric (skip for all marshes and Pine Flat) ?A Vegetation is close to reference condition in species present and their proportions. Lower strata composed of appropriate species, with exotic plants absent or sparse within the assessment area. ®B Vegetation is different from reference condition in species diversity or proportions, but still largely composed of native species characteristic of the wetland type. This may include communities of weedy native species that develop after clearcutting or clearing. It also includes communities with exotics present, but not dominant, over a large portion of the expected strata. ?C Vegetation severely altered from reference in composition. Expected strata are unnaturally absent or dominated by exotic species or composed of planted stands of non-characteristic species or inappropriately composed of a single species. 16. Vegetative Diversity - assessment area condition metric (evaluate for Non-tidal Freshwater Marsh only) ®A Vegetation diversity is high and is composed primarily of native species (< 10% cover of exotics). ?B Vegetation diversity is low or has > 10% to 50% cover of exotics. ?C Vegetation is dominated by exotic species (> 50 % cover of exotics). 17. Vegetative Structure - assessment area/wetland type condition metric 17a. Is vegetation present? ®Yes ?No If Yes, continue to 17b. If No, skip to Metric 18. 17b. Evaluate percent coverage of vegetation for all marshes only. Skip to 17c for non-marsh wetlands. ?A ? 25% coverage of vegetation ?B < 25% coverage of vegetation 17c. Check a box in each column for each stratum. Evaluate this portion of the metric for non-marsh wetlands. Consider structure in airspace above the assessment area (AA) and the wetland type (WT) separately. AA WT ?A ?A Canopy closed, or nearly closed, with natural gaps associated with natural processes ?B ?B Canopy present, but opened more than natural gaps ®C ®C Canopy sparse or absent ®A ®A Dense mid-story/sapling layer ?B ?B Moderate density mid-story/sapling layer ?C ?C Mid-story/sapling layer sparse or absent ®A ®A Dense shrub layer ?B ?B Moderate density shrub layer ?C ?C Shrub layer sparse or absent ?A ?A Dense herb layer ®B ®B Moderate density herb layer ?C ?C Herb layer sparse or absent 18. Snags - wetland type condition metric ?A Large snags (more than one) are visible (> 12 inches DBH, or large relative to species present and landscape stability). ®B NotA 19. Diameter Class Distribution - wetland type condition metric ?A Majority of canopy trees have stems > 6 inches in diameter at breast height (DBH); many large trees (> 12 inches DBH) are present. ®B Majority of canopy trees have stems between 6 and 12 inches DBH, few are > 12 inch DBH. ?C Majority of canopy trees are < 6 inches DBH or no trees. 20. Large Woody Debris - wetland type condition metric Include both natural debris and man-placed natural debris. ?A Large logs (more than one) are visible (> 12 inches in diameter, or large relative to species present and landscape stability). ®B NotA 21. Vegetation/Open Water Dispersion - wetland type/open water condition metric (evaluate for Non-Tidal Freshwater Marsh only) 22. Hydrologic Connectivity- assessment area condition metric Evaluate for riverine wetlands only. Examples of activities that may severely alter hydrologic connectivity include intensive ditching, fill, sedimentation, channelization, diversion, man-made berms, beaver dams, and stream incision. ®A Overbank and overland flow are not severely altered in the assessment area. ?B Overbank flow is severely altered in the assessment area. ?C Overland flow is severely altered in the assessment area. ?D Both overbank and overland flow are severely altered in the assessment area. Notes Dry conditions at time of observation. NC WAM Wetland Rating Sheet Accompanies User Manual Version 3.0 Rating Calculator Version 3.0 Wetland Site Name BDMB- HU1A- Zero Order Date of Assessment 6/2/10 IiVICY IVVVQI?- Wetland Type Headwater Forest Assessor Name/Organization LMG Presence of stressor affecting assessment area (Y/N) YES Notes on Field Assessment Form (Y/N) YES Presence of regulatory considerations (Y/N) YES Wetland is intensively managed (Y/N) NO Assessment area is located within 50 feet of a natural tributary or other open water (Y/N) NO Assessment area is substantially altered by beaver (Y/N) NO Sub-function Ratina Summar Function Sub-function Metrics Rating Hydrology Surface Storage and Retention Condition HIGH Sub-surface Storage and Retention Condition MEDIUM Water Quality Pathogen Change Condition HIGH Condition/Opportunity HIGH Opportunity Presence (Y/N) NO Particulate Change Condition HIGH Condition/Opportunity NA Opportunity Presence (Y/N) NA Soluble Change Condition HIGH Condition/Opportunity HIGH Opportunity Presence (Y/N) NO Physical Change Condition LOW Condition/Opportunity LOW Opportunity Presence (Y/N) NO Pollution Change Condition NA Condition/Opportunity NA Opportunity Presence (Y/N) NA Habitat Physical Structure Condition HIGH Landscape Patch Structure Condition HIGH Vegetation Composition Condition MEDIUM Function Ratina Summar Function Metrics Rating Hydrology Condition HIGH Water Quality Condition HIGH Condition/Opportunity HIGH Opportunity Presence (Y/N) NO Habitat Condition HIGH Overall Wetland Rating HIGH (Version June 2009) AGREEMENT TO ESTABLISH THE BACHELORS DELIGHT MITIGATION BANK IN ONSLOW COUNTY, NORTH CAROLINA (USACE Action ID No. 2009-00832) This Mitigation Banking Instrument (MBI) is made and entered into on the day of , 2010, by the Weyerhaeuser Real Estate Development Co. (WREDCO), hereinafter Sponsor, and the U. S. Army Corps of Engineers (Corps), and each of the following agencies, upon its execution of this NMI, the Environmental Protection Agency (EPA), the U. S. Fish and Wildlife Service (FWS), the National Marine Fisheries Service (NMFS), the North Carolina Wildlife Resources Commission (NCWRC), the North Carolina Division of Coastal Management (NCDCM), and the North Carolina Division of Water Quality (NCDWQ). The Corps, together with the State and Federal agencies that execute this NMI, are hereinafter collectively referred to as the Interagency Review Team (IRT). WHEREAS the purpose of this agreement is to establish a mitigation bank (Bank) providing compensatory mitigation for unavoidable wetland impacts separately authorized by Section 404 Clean Water Act permits and /or Section 10 of the Rivers and Harbors Act permits in appropriate circumstances; WHEREAS the Sponsor has entered into a Memorandum of Agreement (MOA) (dated October 2010) with the Board of Trustees of the Endowment Fund of North Carolina State University (ENDOWMENT FUND) and NC State Natural Resources Foundation, Inc. (FOUNDATION) to implement and operate a wetland and stream mitigation bank, a subset of which is located on property owned by the ENDOWMENT FUND (see attached survey); WHEREAS the Sponsor is the record owner of that certain parcel of land containing approximately 252 acres located in Onslow County, North Carolina, described in the Bachelors Delight Mitigation Bank Restoration Plan (October 2010 Mitigation Plan), and as shown on the attached survey (Property A); WHEREAS Endowment Fund is the record owner of that certain parcel of land containing approximately 111 acres, located in Onslow County, North Carolina, described in the Bachelors Delight Mitigation Bank Restoration Plan (Mitigation Plan), and as shown on the attached survey (Property B); WHEREAS the agencies comprising the IRT agree that the combined sites totaling 363 acres (Property A and Property B as identified above) are a suitable mitigation bank site, and that implementation of the Mitigation Plan is likely to result in net gains in wetland and/or stream functions at the Bank site, and have therefore approved the Mitigation Plan; WHEREAS the Foundation has certain rights regarding the use and management of the Bank site under the MOA referenced above with the Endowment Fund and WREDCO; (Version June 2009) THEREFORE, it is mutually agreed among the parties to this agreement that the following provisions are adopted and will be implemented upon signature of this MBI. Section L• General Provisions A. The Sponsor is responsible for assuring the success of the restoration, enhancement, and preservation activities at the Bank site, and for the overall operation and management of the Bank. The Sponsor assumes the legal responsibility for providing the compensatory mitigation once a permittee secures credits from the Sponsor and the DE receives documentation that confirms the Sponsor has accepted responsibility for providing the required compensatory mitigation. B. The goal of the Bank is to restore, enhance, and preserve first order streams, zero order streams, riparian (non-riverine) wetlands, and non-riparian wetlands and their functions to compensate in appropriate circumstances for unavoidable wetland and stream impacts authorized by Section 404 of the Clean Water Act permits and or Section 10 of the Rivers and Harbors Act permits in circumstances deemed appropriate by the Corps after consultation, through the permit review process, with members of the IRT. C. Use of credits from the Bank to offset wetland impacts authorized by Clean Water Act permits must be in compliance with the Clean Water Act and implementing regulations, including but not limited to the 404(b)(1) Guidelines, the National Environmental Policy Act, and all other applicable Federal and State legislation, rules and regulations. This agreement has been drafted in accordance with the regulations for Compensatory Mitigation for Losses of Aquatic Resources effective June 9, 2008 (33 CFR Parts 325 and 332) (Mitigation Rule"). D. The IRT shall be chaired by the District Engineer (DE) of the U. S. Army Corps of Engineers, Wilmington District. The IRT shall review documentation for the establishment of mitigation banks. The IRT will also advise the DE in assessing monitoring reports, recommending remedial measures, approving credit releases, and approving modifications to this instrument. The IRT's role and responsibilities are more fully set forth in Sections 332.8 of the Mitigation Rule. The IRT will work to reach consensus on its actions. E. The DE, after consultation with the appropriate Federal and State review agencies through the permit review process, shall make final decisions concerning the amount and type of compensatory mitigation to be required for unavoidable, permitted wetland impacts, and whether or not the use of credits from the Bank is appropriate to offset those impacts. In the case of permit applications and compensatory mitigation required solely under the Section 401 Water Quality Certification rules of North Carolina, the N.C. Division of Water Quality (NCDWQ) will determine the amount of credits that can be withdrawn from the Bank. F. The parties to this agreement understand that a watershed approach to establish compensatory mitigation must be used to the extent appropriate and practicable. Where practicable, in-kind compensatory mitigation is preferred. (Version June 2009) Section II: Geographic Service Area The Geographic Service Area (GSA) is the designated area within which the bank is authorized to provide compensatory mitigation required by DA permits. The GSA for this Bank shall include the White Oak River Basin, Hydrologic Unit 03030001 in North Carolina (refer to Figure 4 of the Mitigation Plan). Note that following 14-digit Hydrologic Unit Codes (HUCs) of the White Oak River Basin are excluded from the identified GSA: (1) 03030001040005; (2) 03030001040010; and (3) 03030001040020. The service area is based on the location and scope of the project which will generate tangible water quality benefits in one of the main tributaries of the White Oak River through the cessation of agri cultural/silvi cultural land use activities and the restoration of headwater stream and wetland ecosystems. Use of a Bank site to compensate for impacts beyond the GSA (including areas within the excluded 14-digit HUCs identified above) may be considered by the Corps or the permitting agency on a case-by-case basis. Section III: Mitigation Plan Any Mitigation Plan submitted pursuant to this agreement must contain the information listed in 332.4(c)(2) through (14) of the Compensatory Mitigation Rule. A. The Bank site is a currently managed for silvicultural and agricultural production. A more detailed description of the baseline conditions on the site is contained in the Mitigation Plan. B. The Sponsor will perform work described on Section 4 and Section 5 of the Mitigation Plan, including 9,679 linear feet (If) of Priority I stream restoration, 7,0821f of zero-order stream restoration, 5,928 if of Level II stream enhancement, and 11,4001f of stream preservation. Additional work within the Bank will restore 60 acres (ac.) of riparian (non-riverine) wetlands and 85 ac. of non-riparian wetlands. A total of 28 ac. of riparian (non-riverine) wetland enhancement; 48 ac. of riparian (non-riverine) wetland preservation; 13 ac. of non-riparian wetland preservation; and 129 acres of stream buffer/upland buffer will also be included within the Bank. The work associated with the Bank will include backfilling of existing ditches, construction of new stream channels, and planting of native hardwood seedlings. The purpose of this work, and the objective of the Bank, is to restore, enhance, and preserve the wetlands and stream systems associated with headwaters of Bachelors Delight Swamp. Development of the Bank will reduce nutrient inputs, stormwater discharge, and flow velocities in a watershed that is experiencing rapid development. C. The Sponsors shall monitor the Bank Site as described in Section 7 of the Mitigation Plan, until such time as the IRT determines that the success criteria described in Section 7 of the Mitigation Plan have been met. (Version June 2009) D. The members of the IRT will be allowed reasonable access to the Property for the purposes of inspection of the Property and compliance monitoring of the Mitigation Plan. Section IV: Reporting A. The Sponsor shall submit to the DE, for distribution to each member of the IRT, an annual report describing the current condition of the Bank and the condition of the Bank in relation to the success criteria in the Mitigation Plan. The Sponsor shall provide to the DE any monitoring reports described in Section 7 of the Mitigation Plan. B. The Sponsor shall provide ledger reports documenting credit transactions as described in Section VIII of this NMI. C. Each time an approved credit transaction occurs, the Sponsor must notify the DE within 30 days of the transaction. Section V: Remedial Action A. The DE shall review the monitoring reports, and may, at any time, after consultation with the Sponsor and the IRT, direct the Sponsor to take remedial action at the Bank site. Remedial action required by the DE shall be designed to achieve the success criteria specified in the Mitigation Plan. All remedial actions required under this section shall include a work schedule and monitoring criteria that will take into account physical and climactic conditions. B. The Sponsor shall implement any remedial measures required pursuant to the above. C. In the event the Sponsor determines that remedial action may be necessary to achieve the required success criteria, it shall provide notice of such proposed remedial action to all members of the IRT. No remedial actions shall be taken without the concurrence of the DE, in consultation with the IRT. Section VI: Use of Mitigation Credits Description of Wetland Community Types: A. Wetland community types found in a mitigation bank will be described in accordance with the procedures found in the NC Wetland Assessment Method (NC WAM, USACE, 2007). It is expected that impacts to the NC WAM types listed below will be compensated by the Mitigation Types as listed in order to qualify as "In-Kind" mitigation. Exceptions to the use of "In-Kind" mitigation may be allowed at the discretion of the permitting agencies on a case-by-case basis. (Version June 2009) Table 1. Wetland Community Types Mitigation Type NCWAM Type CAMA Coastal Wetland Salt/Brackish Marsh* Riparian (Riverine) Riverine Swamp Forest/Non-Tidal Freshwater Marsh, Tidal Freshwater Marsh Riparian (Non-Riverine) Bottomland Hardwood Forest, Headwater Wetland, Flood- Plain Pool, Mountain Bog* Non-Riparian Non-Riverine Swamp Forest, Seep, Small Basin Wetland, Pocosins, Estuarine Woody, Pine Flat, Pine Savannah, Hardwood Flat Table 2. Mitigation Types and Quantities (acres/If) Streams (linear feet) Priority 1 Zero Order Enhancement Type Restoration Restoration (Level 11) Preservation SBCF Hewitts Branch 5,103 500 4,900 656 Huffmans Branch 3,445 1,404 2,000 1,200 431 Bachelors Delight Swamp 4,777 3,428 5,300 Half Moon Creek 1,131 901 147 TOTAL 9,679 7,082 5,928 11,400 1,234 RATIO 1:1 1:1 1.5:1 2.5:1 NA CREDITS 9,679 7,082 3,952 4,560 1,234 GRAND TOTAL 26,507 Wetlands (acres) Proposed Type Acreage Ratio Credits" Riparian Restoration 60 1:1 60r Riparian Enhancement 28 2:1 14re Riparian Wetland Preservation 48 5:1 10re Non-Riparian Restoration 85 1:1 85r Non-Riparian Preservation 13 7:1 2re SBCF/Upland Buffer 129 NA 0 TOTAL 363 171 *r=restoration credit; re= restoration-equivalent credit (Version June 2009) Table 3. Mitigation Credits by Stream and Wetland Type Mitigation Type Quantity (If/ac) Credits Stream 34,089 26,507* Riparian (Non-Riverine) Wetland 136 84 Non-Riparian Wetland 98 87 *Includes credits derived from Stream Buffer Correction Factor (SBCF) B. It is anticipated by the parties that in most cases in which the DE, after consultation with the IRT, has determined that mitigation credits from the Bank may be used to offset wetland impacts authorized by Section 404 permits and/or Section 10 permits, that the Restoration Equivalents, as enumerated above, constitute credits that are considered to be equal to restoration credits for the purposes of compensatory mitigation. Therefore, the use of Restoration credits or Restoration Equivalents credits, or any combination thereof, is acceptable to the DE for any permit requirement so long as the required amount of credits are debited for a given mitigation requirements. It is also understood that in order to satisfy mitigation requirements imposed by the NC Division of Water Quality, restoration impact amounts must be at a minimum of 1:1 such that for every one acre of impact, at least one acre of mitigation must be in the form of restoration. Additionally, decisions regarding stream mitigation will be made consistent with current policy and guidance and will be made on a case by case basis. Wetland and stream compensation ratios are determined by the DE on a case-by-case basis based on considerations of functions of the wetlands and/or streams impacted, the severity of the wetland and/or stream impacts, the relative age of the mitigation site, whether the compensatory mitigation is in-kind, and the physical proximity of the wetland and/or stream impacts to the Bank site. C. Notwithstanding the above, all decisions concerning the appropriateness of using credits from the Bank to offset impacts to waters and wetlands, as well as all decisions concerning the amount and type of such credits to be used to offset wetland and water impacts authorized by Department of the Army permits, shall be made by the DE, pursuant to Section 404 of the Clean Water Act and implementing regulations and guidance, after notice of any proposed use of the Bank to the members of the IRT, and consultation with the members of the IRT concerning such use. Notice to and consultation with the members of the IRT shall be through the permit review process. Section VII: Credit Release Schedule All credit releases must be approved by the DE, in consultation with the IRT, based on a determination that required success criteria have been achieved. A. Credit Release Schedule for Forested Wetlands: If deemed appropriate by the IRT, fifteen percent (15%) of the Bank's total restoration credits shall be available for sale immediately upon completion of all of the following: (Version June 2009) 1. Execution of this MBI by the Sponsor, the DE, and other agencies eligible for membership in the IRT who choose to execute this agreement; 2. Approval of the final Mitigation Plan; 3. Mitigation bank site has been secured; 4. Delivery of the financial assurance described in Section IX of this MBI; and 5. Recordation of the long-term protection mechanism described in Section X of this MBI, as well as a title opinion covering the property acceptable to the DE. The Sponsor must complete the initial physical and biological improvements to the Bank site pursuant to the Mitigation Plan no later than the first full growing season following initial debiting of the Bank. Subject to the Sponsor's continued satisfactory completion of all required success criteria and monitoring, additional restoration mitigation credits will be available for sale by the Sponsor on the following schedule: 1. 15 % upon completion of all initial physical and biological improvements made pursuant to the Mitigation Plan (total 30%); 2. 10% after first year, if interim success measures are met (total 40%); 3. 10% after second year, if interim success measures are met (total 50%); 4. 10% after third year, if interim success measures are met (total 60%); 5. 10% after fourth year, if interim success measures are met (total 70%); 6. 10% after fifth year, if Success Criteria are met (total 80%); 7. 10% after sixth year, if vegetative Success Criteria are met (90%); and 8. 10% after seventh year, if vegetative Success Criteria are met (100%). Provided that all Success Criteria are met, the IRT may allow the Sponsor to discontinue hydrologic monitoring after the fifth year. The Sponsor will be required to monitor vegetation for an additional two years after the fifth year for a total of seven years. B. Credit Release Schedule for Streams: The following credit release schedule applies only to those stream projects where Restoration or Enhancement I has been performed where pattern, dimension, and profile, or dimension and profile (respectively) have been improved. Projects constructed on the outer coastal plain that are subject to the Coastal Plain Information Paper (USACE/DWQ 2007) where an engineered stream channel was not constructed, will be subject to the criteria enumerated for wetlands above. If deemed appropriate by the IRT, fifteen percent (15%) of the Bank's total stream credits shall be available for sale immediately upon completion of all of the following: 1. Execution of this MBI by the Sponsor, the DE, and other agencies eligible for membership in the IRT who choose to execute this agreement; 2. Approval of the final Mitigation Plan; 3. Mitigation bank site has been secured; 4. Delivery of the financial assurance described in Section IX of this MBI; and (Version June 2009) 5. Recordation of the long-term protection mechanism described in Section X of this NMI, as well as a title opinion covering the property acceptable to the DE. Table 4A. Credit Release Schedule for Wetlands Percentage of Wetland Cumulative Projected Credits Task Credits Released (% Credits Completion Date Released cumulative) Released 1.0 Signing of the NMI; 1/15/11 15(15) 25.6 25.6 Recordation of Conservation Easement Deed; Delivery of Financial Assurances 2.0 Completion of Physical and 2/2012 15(30) 25.6 51.2 Biological Improvements 3.0 Year 1: Fulfill Success 1/2013 10(40) 17.1 68.3 Criteria 4.0 Year 2: Fulfill Success 1/2014 10(50) 17.1 85.4 Criteria 5.0 Year 3: Fulfill Success 1/2015 10(60) 17.1 102.5 Criteria 6.0 Year 4: Fulfill Success 1/2016 10(70) 17.1 119.6 Criteria 7.0 Year 5: Fulfill Success 1/2017 10(80) 17.1 136.7 Criteria 8.0 Year 6: Fulfill Success 1/2018 10(90) 17.1 153.8 Criteria 9.0 Year 7: Fulfill Success 1/2019 10(100) 17.2 171 Criteria TOTAL 100% 171 Subject to the Sponsor's continued satisfactory completion of all required success criteria and monitoring, additional stream credits will be available for sale by the Sponsor on the following schedule: 1. 15 % upon completion of all initial physical and biological improvements made pursuant to the Mitigation Plan (total 30%); 2. 10% after first year, provided channel is stable and all other success measures are met (total 40%); 3. 10% after second year, provided channel is stable and all other success measures are met (total 50%); 4. 10% after third year, provided channel is stable and all other success measures are met (total 60%); 5. 10% after fourth year, provided channel is stable and all other success measures are met (total 70%); 6. 15% after fifth year, provided channel is stable and all other success measures are met (total 85%). (Version June 2009) A reserve of 15% of the Bank's total stream credits shall be released any time after two bank-full events have occurred, in separate years, provided the channel is stable and all other Success Criteria are met. In the event that less than two bank-full events occur during the monitoring period, remaining credit release shall be at the discretion of the IRT. Table 4B. Credit Release Schedule for Streams Projected Percentage of Wetland Credits Cumulative Task Completion Date Credits Released (% Released Credits cumulative) Released 1.0 Signing of the NMI; 1/15/11 15 (15) 3,976 3,976 Recordation of Conservation Easement Deed; Delivery of Financial Assurances 2.0 Completion of Physical and 2/2012 15 (30) 3,976 7,952 Biological Improvements 3.0 Year 1: Fulfill Success 1/2013 10(40) 2,651 10,603 Criteria 4.0 Year 2: Fulfill Success 1/2014 10(50) 2,650 13,253 Criteria 5.0 Year 3: Fulfill Success 1/2015 10(60) 2,651 15,904 Criteria 6.0 Year 4: Fulfill Success 1/2016 10(70) 2,650 18,555 Criteria 7.0 Year 5: Fulfill Success 1/2017 15(85) 3,976 22,531 Criteria 8.0 Documentation of Two TBD 15(100) 3,976 26,507 Bank-full Events in Separate Years TOTAL 100% 26,507 Section VIII: Accounting Procedures A. The Sponsor shall develop accounting procedures acceptable to the IRT for maintaining accurate records of debits made from the Bank. Such procedures shall include the generation of a ledger by the Sponsor showing credits used at the time they are debited from the Bank. All ledger reports shall identify credits debited and remaining by type of credit and shall include for each reported debit the Corps ORM ID number for the permit for which the credits were utilized and the permitted impacts for each resource type. Each time an approved credit transaction occurs, the Sponsor must notify the DE within 30 days of the transaction. B. The Sponsor shall prepare an annual ledger report, on each anniversary of the date of execution of this agreement, showing all credits used, any changes in credit availability (e.g., (Version June 2009) additional credits released, credit sales suspended), and the beginning and ending balance of credits remaining. The Sponsor shall submit the annual report to the DE, for distribution to each member of the IRT, until such time as all of the credits have been utilized, or this agreement is otherwise terminated. Section IX: Financial Assurances A. The Sponsor shall provide financial assurances in a form acceptable to the IRT sufficient to assure completion of all mitigation work, required reporting and monitoring, and any remedial work required pursuant to this NMI. These financial assurances are provided in the form of two performance bonds. A construction bond, in the sum of $500,000, represents 30% of the projected construction, planting, and contingency costs associated with the activities described in the Mitigation Plan. The monitoring bond, in the sum of $70,000, represents 10% of the projected monitoring costs for the seven (7) year schedule described in the Mitigation Plan. B. Financial assurances shall be payable at the direction of the DE to his designee or to a standby trust. Financial assurances structured to provide funds to the Corps of Engineers in the event of default by the Bank Sponsor are not acceptable. C. A financial assurance must be in the form that ensures that the DE receives notification at least 120 days in advance of any termination or revocation. Section X: Long-Term Protection A. The North Carolina State Natural Resources Foundation (Foundation), a registered 501(c)3 entity, will serve as the holder of the conservation easement (CE) for the Bank. The Foundation will maintain the CE in perpetuity and provide for the long-term protection of the land through annual monitoring activities. Title to the land will reside with the current owners, WREDCO (Tract A) and The Endowment Fund of North Carolina State University (Tract B). Refer to the attached conservation easement plats for both tracts (Appendix B). The CE shall be perpetual, preserve all natural areas, and prohibit all use of the property inconsistent with its use as mitigation property, including any activity that would materially alter the biological integrity or functional and educational value of wetlands or streams within the Bank site, consistent with the Mitigation Plan. The purpose of the CE will be to assure that future use of the Bank site will result in the restoration, protection, maintenance and enhancement of wetland functions described in the Mitigation Plan. B. The Sponsor shall deliver a title opinion acceptable to the DE covering the mitigation property. The property shall be free and clear of any encumbrances that would conflict with its use as mitigation, including, but not limited to, any liens that have priority over the recorded preservation mechanism. 10 (Version June 2009) C. Subsequent to the recording of the CE, the Sponsor may convey the Bank Site property either in fee or by granting an easement to a qualified land trust, state agency, or other appropriate nonprofit organization. The Sponsor is responsible for ensuring that that the CE is re-recorded to ensure that it remains within the chain of title. The terms and conditions of this conveyance shall not conflict with the intent and provisions of the CE nor shall such conveyance enlarge or modify the uses specified in the CE. The CE must contain a provision requiring 60 day advance notification to the DE before any action is taken to void or modify the CE, including transfer of title to, or establishment of any other legal claims over, the project site. Section XI: Long-term Management A. The Foundation (as identified above) will be responsible for the long-term management of the site. The primary objective of the long-term management is to ensure the protection of the site in its natural state. B. An endowment will be provided to the Foundation by the Sponsor to assist with the long- term management expenses of the Bank site. Section XIL• Default and Closure A. It is agreed to establish and/or maintain the Bank site until (i) credits have been exhausted or banking activity is voluntarily terminated with written notice by the Sponsor provided to the DE and other members of the IRT; and (ii) it has been determined and agreed upon by the DE and IRT that the debited Bank site has satisfied all the conditions herein and in the Mitigation Plan. If the DE determines that the Bank site is not meeting performance standards or complying with the terms of the instrument, appropriate action will be taken. Such actions may include, but are not limited to, suspending credit sales, adaptive management, decreasing available credits, utilizing financial assurances, and terminating the instrument. B. Any delay or failure of Bank Sponsor shall not constitute a default hereunder if and to the extent that such delay or failure is primarily caused by any act, event or conditions beyond the Sponsor's reasonable control and significantly adversely affects its ability to perform its obligations hereunder including: (i) acts of God, lightning, earthquake, fire, landslide, or interference by third parties; (ii) condemnation or other taking by any governmental body; (iii) change in applicable law, regulation, rule, ordinance or permit condition, or the interpretation or enforcement thereof, (iv) any order, judgment, action or determination of any federal, state or local court, administrative agency or government body; or (v) the suspension or interruption of any permit, license, consent, authorization or approval. If the performance of the Bank Sponsor is affected by any such event, Bank Sponsor shall give written notice thereof to the IRT as soon II (Version June 2009) as is reasonably practicable. If such event occurs before the final availability of all credits for sale, the Sponsor shall take remedial action to restore the property to its condition prior to such event, in a manner sufficient to provide adequate mitigation to cover credits that were sold prior to such delay or failure to compensate for impacts to waters, including wetlands, authorized by Department of the Army permits. Such remedial action shall be taken by the Sponsor only to the extent necessary and appropriate, as determined by the IRT. C. At the end of the monitoring period, upon satisfaction of the performance standards, the Sponsor may submit a request to close out the bank site to the DE. The DE, in consultation with the IRT, shall use best efforts to review and comment on the request within 60 days of such submittal. If the DE determines the Sponsor has achieved the performance standards in accordance with the mitigation plan and all obligations under this NMI, the DE shall issue a close out letter to the Sponsor. Section XIII: Miscellaneous A. Any agency participant may terminate its participation in the IRT with notice in writing to all other parties to this agreement. Termination shall be effective seven (7) days from placing written notices in the United States mail. Member withdrawal shall not affect any prior sale of credits and all remaining parties shall continue to implement and enforce the terms of this NMI. B. Modification of this MBI shall be in accordance with the procedures set forth in 332.8 of the mitigation rule. C. No third party shall be deemed a beneficiary hereof and no one except the signatories hereof, their successors and assigns, shall be entitled to seek enforcement hereof. D. This MBI constitutes the entire agreement between the parties concerning the subject matter hereof and supersedes all prior agreements or undertakings. E. In the event any one or more of the provisions contained in this MBI are held to be invalid, illegal or unenforceable in any respect, such invalidity, illegality or unenforceablility will not affect any other provisions hereof, and this MBI shall be construed as if such invalid, illegal or unenforceable provision had not been contained herein. F. This NMI shall be governed by and construed in accordance with the laws of North Carolina and the United States as appropriate. G. This MBI may be executed by the parties in any combination, in one or more counterparts, all of which together shall constitute but one and the same instrument. H. The terms and conditions of this MBI shall be binding upon, and inure to the benefit of the parties hereto and their respective successors. 12 (Version June 2009) 1. All notices and required reports shall be sent by regular mail to each of the parties at their respective addresses, provided below. Sponsor: Mr. Taylor Downey Weyerhaeuser Real Estate Development Company 1412 Eatonton Hwy Suite 700 Madison, GA 30850 Corps: Mr. Mickey Sugg U. S. Army Corps of Engineers Regulatory Division 69 Darlington Avenue Wilmington, NC 28403 EPA: Ms. Jennifer Derby Wetlands Section - Region IV Water Management Division U. S. Environmental Protection Agency 61 Forsyth Street, SW Atlanta, Georgia 30303 FWS: Mr. Pete Benjamin U.S. Fish and Wildlife Service Fish and Wildlife Enhancement Post Office Box 33726 Raleigh, North Carolina 27636-3726 NMFS: Mr. Ron Sechler National Marine Fisheries, NOAA Habitat Conservation Division Pivers Island Beaufort, North Carolina 28516 NCWRC: Ms. Molly Ellwood North Carolina Wildlife Resources Commission 127 Cardinal Drive Extension Wilmington, NC 28405 13 (Version June 2009) NCDCM: Mr. Steve Sollod North Carolina Division of Coastal Management 127 Cardinal Drive Extension Wilmington, NC 28405 NCDWQ: Ms. Cyndi Karoly NC Division of Water Quality North Carolina Department of Environment and Natural Resources Post Office Box 29535 Raleigh, NC 27626-0535 14 (Version June 2009) IN WITNESS WHEREOF, the parties hereto have executed this Agreement entitled "Agreement To Establish The Bachelors Delight Mitigation Bank in Onslow County, North Carolina": Sponsor: By: U.S. Army Corps of Engineers: Date: By: Date: 15 (Version June 2009) IN WITNESS WHEREOF, the parties hereto have executed this Agreement entitled "Agreement To Establish The Bachelors Delight Mitigation Bank In Onslow County, North Carolina": U.S. Environmental Protection Agency: By: Date: U.S. Fish and Wildlife Service: By: Date: National Marine Fisheries Service: By: Date: N.C. Division of Water Quality: By: Date: N.C. Wildlife Resources Commission: By: Date: N.C. Division of Coastal Management: By: Date: 16 (Version June 2009) List of Appendices Appendix A: Bachelors Delight Stream and Wetland Mitigation Bank - Final Mitigation Plan (October 2010) Appendix B: Conservation Easement Plats (Tract A and Tract B) Appendix C: Map - Geographic Service Area Appendix D: Construction Costs Appendix E: Maintenance and Monitoring Costs Appendix F: Performance Bonds Appendix G: Conservation Easement Deed 17 STATE OF NORTH CAROLINA COUNTY OF ONSLOW /NFFMW FUIMSf R I, REVIEW OFFICER OF ONSLOW A'G'l4A04 ?.M COUNTY, CERTIFY TO THE BEST OF MY KNOWLEDGE AND BELIEF THE o A MAP/PLAT TO WHICH THIS CERTIFICATION IS AFFIXED MEETS THE ? A STATUTORY REQUIREMENTS FOR RECORDING. X REVIEW OFFICER X DATE CKSONWIlE rn d m a 8 FILED FOR REGISTRATION AT M O,CLOCK CAW LEJMW THIS OF AD e 10 IN PLAT CABINET -SLIDE / AT VICINITY MAP - NOT TO SCALE o_ REGISTER OF DEEDS IGC SURVEYOR'S NOTES: 1. BEARINGS BASED ON NC GRID (NAD 83) CORS 95, 2. REFERENCES: DEED BOOK 2710 PAGE 918, DEED BOOK 516 PAGE 408. 3. SURVEYOR HAS MADE NO INVESTIGATION OR INDEPENDENT SEARCH FOR EASEMENTS OF RECORD, ENCUMBRANCES, RESTRICTIVE COVENANTS, OWNERSHIP, TITLE EVIDENCE, OR ANY OTHER FACTS THAT AN ACCURATE AND CURRENT TIRE SEARCH MAY DISCLOSE 4. SUBSURFACE AND ENVIRONMENTAL CONDITIONS WERE NOT EXAMINED OR CONSIDERED AS A PART OF THIS SURVEY. NO STATEMENT IS MADE CONCERNING THE EXISTENCE OF UNDERGROUND OR OVERHEAD CONTAINERS OR FACILITIES THAT MAY AFFECT THE USE OR DEVELOPMENT OF THIS TRACT. 5. SUBJECT TO ALL EASEMENTS, RIGHT OF WAYS, AND OR ENCUMBRANCES OF RECORD THAT MAY EFFECT THIS PROPERTY. % / WF / WEYERHAEUSER REAL ESTATE / DEVELOPMENT COMPANY DEED BOOK 2710 PAGE 916 ? i WF THE BOARD OF TRUSTEES NCSU DEED BOOK 516 PAGE 409 SURVEYOR'S CERTIFICATION: EGEND I, DAVID L JONES, JR, L-3672, CERTIFY THAT THIS PLAT WAS DRAWN UNDER MY SUPERVISION FROM AN ACTUAL SURVEY MADE UNDER MY NOW/FORMERLY SUPERVISION FROM INFORMATION SHOWN IN DEED BOOKS AND (OR) IRONRODSET MAPS REFERENCED ON THIS PLAT; THAT ONES NOT ACTUALLY IRON ROD FOUND SURVEYED APPEAR AS BROKEN LINES AND WERE PLOTTED FROM INFORMATION AS NOTED ON THE PUT; THAT THE RATIO OF PRECISION AS CALCULATED BY LATITUDES AND DEPARTURES WAS GREATER THAN 1:10,000; THAT THE AREA IS COMPUTED BY COORDINATE METHOD; THAT THIS PLAT WAS PREPARED IN ACCORDANCE WITH G.S. 47-30 AS AMENDED. WITNESS MY ORIGINAL SIGNATURE, LICENSE NUMBER, AND SEAL THIS THEY OF Dec AD.,---Z-..o THIS SURVEY IS OF ANOTHER CATEGORY, SUCH AS THE RECOMBINATION OF EXISTING PARCELS, A COURT-ORDERED SURVEY, OR OTHER EXCEPTION TO THE DEFINITION OF SUBDIVISION. THAT THE CPS SURVEY MADE WAS UNDER MY SUPERVISION AND THE FOLLOWING INFORMATION WAS USED TO PERFORM THIS SURVEY. i J / CLASS OF SURVEY. C - RURAL AND FARMLAND SURVEY POSITIONAL ACCURACY: 0.098 TYPE OF CPS FIELD PROCEDURE OPUS DATES OF SURVEY: JANUARY 3, 2007 DATUM/EPOCH: NC GRID NAD53 COBS' 96 PUBUSHED/FIXED-CONTROL USED:;KEWSVILLE-CORS'_, GEOID MODEU GEOID 03 ' '. COMBINED GRID FACTOR: 0.999899370' UNITS: U.S. SURVEY FEET ' WITNESS MY ORIGINAL SIGNATURE, LICENSE NUMBER AND SEAL DAY OF DAVID-. JONES, JR. PROFESSIONAL LAND SCALE: 1'= 200' 0 100 200 460 600 4 N14OM&CREM 243 NORTH FRONT STREET WILMINGTON, NORTH CAROLINA 28401 TELEPHONE: (910) 251-6665 FAX: (910) 794-1154 NORTH CAROLINA FIRM LICENSE NUMBER: C-0342 CONSERVATION EASEMENT SURVEY OF 20.81 ACRES FOR THE BOARD OF TRUSTEES NCSU PORTION OF HOFMANN FOREST DEED BOOK 516 PAGE 408 RICHLANDS TOWNSHIP - ONSLOW COUNTY - NORTH CAROLINA JULY 6, 2010 JOB NUMBER: DD910-0166 SCALE: 1' = 200' CAD NUMBER: VM101-009100166 PIES: DU PARTY CEIIEF: JR/AR CAD TECH. ACS FEW BOOK/PAGE: W1206/31-.. DRAWING NUMBER: 2010-052 SHEET 1 OF 1 m m B 3 0 rc U Z NIP THE BOARD OF TRUSTE DEED BOOK 516 PAC STATE OF NORTH CAROLINA COUNTY OF ONSLOW RENEW OFFICER OF ONSLOW COUNTY, ME BEST OF MY KNOWLEDGE AND BELIEF THE MAP/PLAT IS CQtTIFlCATI ON IS AFFIXED MEETS THE STATUTORY S FOR RECORDING. OFFICER :GISTRATION AT M O,CLOCK _ OF AD _ INET DUDE REGISTER OF DEEDS N gyp{^G?W\\\FVEST p- Y ?, SURVEYOR'S NOTES: 1. BEARINGS BASED ON NC GRID (NAD 83) COPS 96. 2. REFERENCES: DEED BOOK 2710 PAGE 916. DEED BOOK 516 PAGE 408. D VIFORMERLY V ROD SET N ROD FOUND SURVEYOR'S CERTIFICATION: / / i I I i i i i Y i i i i? i/ SCALE: 1" = 300' 0 150 300 800 900 243 NORTH FRONT STREET WILMINGTON, NORTH CAROLINA 28401 TELEPHONE: (910) 251-6665 FAX: (910) 794-1154 NORTH CAROLINA FIRM LICENSE NUMBER: C-0342 r+ 3. SURVEYOR HAS MADE NO INVESTIGATION OR INDEPENDENT SEARCH FOR EASEMENTS OF RECORD, ENCUMBRANCES, RESTRICTIVE COVENANTS, OWNERSHIP, TITLE EVIDENCE, OR ANY OTHER FACTS THAT AN ACCURATE AND CURRENT TITLE SEARCH MAY DISCLOSE 4. SUBSURFACE AND ENVIRONMENTAL CONDITIONS WERE NOT EXAMINED OR CONSIDERED AS A PART OF THIS SURVEY. NO STATEMENT IS MADE CONCERNING THE EXISTENCE OF UNDERGROUND OR OVERHEAD CONTAINERS OR FACILITIES THAT MAY AFFECT THE USE OR DEVELOPMENT OF THIS TRACT. 5. SUBJECT TO ALL EASEMENTS, RIGHT OF WAYS, AND OR ENCUMBRANCES OF RECORD THAT MAY EFFECT THIS PROPERTY. I, DAVID L JONES, JR. L-3672, CERTIFY THAT THIS PLAT WAS DRAWN UNDER MY SUPERVISION FROM AN ACTUAL SURVEY MADE UNDER MY SUPERVISION FROM INFORMATION SHOWN IN DEED BOOKS AND (OR) MAPS REFERENCED ON THIS PLAT; THAT LINES NOT ACTUALLY SURVEYED APPEAR AS BROKEN UNES AND WERE PLOTTED FROM INFORMATION AS NOTED ON THE PLAT; THAT THE PATIO OF PRECISION AS CALCULATED BY LATITUDES AND DEPARTURES WAS GREATER THAN 1:10,000; THAT THE AREA IS COMPUTED BY COORDINATE METHOD; THAT THIS PLAT WAS PREPARED IN ACCORDANCE WITH G.S. 47-30 AS AMENDED. WITNESS MY ORIGINAL SIGNATURE, LICENSE NUMBER, AND SEAL THIS THE-J-DAY OF A.D,-:Xbko THIS SURVEY IS OF ANOTHER CATEGORY, SUCH AS THE RECOMBINATION OF EXISTING PARCELS, A COURT-ORDERED SURVEY, OR OTHER EXCEPTION TO THE DEFINITION OF SUBDIVISION. THAT THE GPS SURVEY MME WAS UNDER MY SUPERVISION AND THE FOLLOWING INFORMATION WAS USED TO PERFORM THIS SURVEY. CLASS OF SURVEY: C - RURAL AND FARMLAND SURVEY POSITIONAL ACCURACY: 0.098 TYPE OF GPS FIELD PROCEDURE: OPUS DATES OF SURVEY: JANUARY 3, 2007 DATUM/EPOCH: NC GRID NAD83 COPS 96 PUBLISHED/FIXED-CONTROL USED: KENANSVILLE COPS GEOID MODEL GEOID 03 COMBINED GRID FACTOR: UNITS: U.S. SURVEY FEET CONSERVATION EASEMENT SURVEY OF 89.98 ACRES FOR THE BOARD OF TRUSTEES NCSU PORTION OF HOFMANN FOREST DEED BOOK 516 PAGE 408 RICHLANDS TOWNSHIP - ONSLOW COUNTY- NORTH CAROLINA JULY 6, 2010 JOB NUMBER: 00910-0166 SCALE: 1" - 300, CAD NUMBER: VM101-009100166 PIS: DU PARTY CHIEF: JR/AK CAD TECH: ACS FIELD BOOK/PAGE: W1206/31-.. DRAWING NUMBER 2u10-053 SHEET 1 OF 1 i i TTT X m m °a a 0 U Z ELEV. 45.10' NO GRID NAD 83 I MATCH L N/F WEYERHAEUSER REAL ESTATE DEVELOPMENT COMPANY DEED BOOK 2710 PAGE 916 --X- - MATCILM V wl w N A TELEPHONE: (910) 251-6665 FAX: (910) 794-1154 NORTH CAROLINA FIRM LICENSE NUMBER: C-0342 CONSERVATION EASEMENT SURVEY FOR WEYERHAEUSER REAL ESTATE DEVELOPMENT COMPANY PORTION OF ONSLOW 19 TRACT RICHLANDS TOWNSHIP - ONSLOW COUNTY - NORTH CAROLINA JULY 6, 2010 LEGEND N/F = NOW/FORMERLY DB = DEED BOOK MB - MAP BOOK PG - PAGE . IRON ROD SET IRF0 =IRON ROD FOUND IPF0 = IRON PIPE FOUND CMFEI = CONCRETE MONUMENT FOUND - - - - - - PROPERTY LINE \ J 30B NUMBER: 06910-0166 SCALE: 1' = 200' CAD NUMBER: VB101-609100166 PLS; DEM PARTY CHIEF: CB,MC,DWAK CAD TECH: ACS FIELD BOOK/PAGE: W1239/16 DRAWING NUMBER: 2010-06- SHEET 6 OF 11 N \ SUNSET COVE DEVELOPMENT INC. DB 2527 PG 580 MB 39 PG 105 kqT%AXe SCALE: I"= 200' C D 243 NORTH FRONT STREET 6 160 260 400 800 WILMINGTON, NORTH CAROLINA 28401 N/f WEYERHAEUSER REAL ESTATE DEVELOPMENT COMPANY DEED BOOK 1710 PAGE 916 Ij , JI -- -Z -- wraHLME or -7- N1'F REYERHAEUSER REAL ESTATE DEVELOPMENT COMPANY DEED BOOK 1710 PACE 916 31 LEGEND i N/F - NOW/FORMERLY DB = DEED BOON MB = MAP BOOT( PG = PAGE • - IRON ROD SET IRF0 - IRON ROD FOUND IPF0 = IRON PIPE FOUND CMFD = CONCRETE MONUMENT FWD -.. - -. -........ = PROPERTY LINE SCALE: 1" = 200' 0 100 200 460 600 Ll022 IRF m \ U Z L92$9L 2 Sy ?' \\\ BEYERHAEUSER REAL ESTATE %l \\ DEVELOPMENT COMPANY / DEED BOO( 2710 PAGE 916 \ i AO 243 NORTH FRONT STREET WILMINGTON, NORTH CAROLINA 28401 TELEPHONE: (910) 251-6665 FAX: (910) 794-1154 NORTH CAROLINA FIRM LICENSE NUMBER: C-0342 CONSERVATION EASEMENT SURVEY FOR WEYERHAEUSER REAL ESTATE DEVELOPMENT COMPANY PORTION OF ONSLOW 19 TRACT RICHLANDS TOWNSHIP - ONSLOW COUNTY - NORTH CAROLINA JULY 6, 2010 JOB NUMBER, OD910-0166 SCALE: 1" - 200' CAD NUMBER: VB101-009100166 PIS: DEM PARTY CHIEF: CB.MC.DWAK CAD TECH: ACS FD LD BOO"AGE: W1239/16 DRAWING NUMBER: 2D`.u-7e9 SHEET 7 OF 11 m W O 6 Z O U U Z RBC N9J N 406820.0690 E 2464896.7085 N 406646.6200 E 2464176.2900 \ N ? N ? N LEGEND / N/F - NOW/FORMERLY 1 DB = DEED BOOK TAB = MAP BOOK PG = PAGE 0 - IRON ROD SET IRF0 - IRON ROD FOUND IPF0 = IRON PIPE FOUND CMFE1 = CONCRETE MONUMENT FOUND .. _...._..... = PROPERTY UNE J SCALE: I"= 200' 6 160 260 400 600 N/P WEYERHAEUSER REAL ESTATE DEVELOPMENT COMPANY DEED BOOK 2710 PAGE 916 N/F RODGERS TRACT DB 958 PG 304 IRF 1. 1V4IQM&CREED 243 NORTH FRONT STREET WILMINGTON, NORTH CAROLINA 28401 TELEPHONE: (910) 251-6665 FAX: (910) 794-1154 NORTH CAROLINA FIRM LICENSE NUMBER: C-0342 N/F WEYERHAEUSER REAL ESTATE DEVELOPMENT COMPANY DEED BOOK 2710 PAGE 916 `V ?g ? ; g-l i CONSERVATION EASEMENT SURVEY FOR WEYERHAEUSER REAL ESTATE DEVELOPMENT COMPANY PORTION OF ONSLOW 19 TRACT RICHLANDS TOWNSHIP - ONSLOW COUNTY - NORTH CAROLINA JULY 6, 2010 JOB NUMBER: 00910-0166 SCALE: 1- - 200' CAD NUMBER: VB101-009100166 PLS: DEM PARTY CHEEF: CB,MC.DWAK CAD TECH: ACS FIELD BOOK/PAGE: W1239/16 DRAWING NUMBER: 201G-OC9 SHEET 8 OF 11 LINE TABLE LINE LENGTH BEARING L1 218.21 N42'13'36"W L2 157.75 N0225'55"E L3 28.13 SB55744W L4 135.08 N7557'53'W L5 134.08 N6736'56'W 1-6 130.21 N5246'48'W 1-7 127.92 N4720'05"W La 63.76 N4720'05"W L9 87.12 N46'5Vl-rW L10 100.86 N4818'06"W L11 35.53 N7254'18'W L12 81.80 N8755'00"W L13 37.03 SBB'41'34"W L14 74.31 S7139'02"W L15 12.99 S7139'02'W L16 69.36 S71 *39'02"W L17 118.72 S7139'02"W L18 126.07 S73'4354'W L19 155.11 N5659'58'W L20 225.39 N3225'50"W L21 55.66 N3711'26"E L22 86.76 N3711'26"E L23 215.38 S8858'18"E L24 79.98 N71 *39'02'E L25 8236 N71'39'00E L26 65.28 N71'39'02"E L27 67.76 N68'41'34"E L28 87.60 N5333'5B"E L29 143.72 S8755'00"E L30 150.06 S7254'1 WE L31 181.24 54818'08"E L32 90.08 S4658'1 7'E L33 62.65 S472W05"E L34 111.27 S4720'05'E L35 68.00 2'46'48'E L36 6296 S5736'56"E L37 53.87 S755r53'E L38 175.04 N655744'E L39 143.28 536'09'01"E L40 98.62 S30'3221'E L41 79.18 S3218'43'E L42 111.68 S0225'56'W L43 13.12 S0225'56'W L44 43.96 S4024'34'E L45 349.94 542'48'13"W L46 366.70 N43'03'55"E L47 418.56 s7r49'43"E L48 20244 N4228'30'E L49 385.82 S85'40'1 0'E L50 359.61 S39'4r05'E L51 90.40 S78'41'21'E L52 25.79 S2505'10'E L53 193.29 S2505'10'E L54 286.88 S7324'01'E L55 135.73 N4201'37"E L56 53.96 N70'42'49"E L57 89.50 S6857'13"E L58 94.73 S3522'52E L59 97.09 S1826'05"E L60 121.28 S741r08'E L61 65.73 N0237'19"E L62 67.86 N44'41'37"E L63 40.22 N8638'02"E L64 99.38 N1020'27'E L65 345.41 578'38'41"E L66 37.47 57504'34"E L67 23.18 56812735"E L68 8.90 S5121'21'E L69 15.62 S2634'39'E L70 109.59 S1114'02"E L73 4.45 58152'20"W L74 56.40 578'48'39"W L75 85.81 N76'45'20'W L76 141.98 N8235'40'W L77 35.48 S5757'57'W L78 76.84 S1700'59"E L79 27.80 S1653'13"W L80 73.11 S33'4742'W L51 LIT 36 S24-4731'W L82 62.60 S43'02'35"W LINE TABLE (CONTINUES) LINE LENGTH BEARING L83 48.31 S4733'20'W L84 53.70 S5923'36"E L55 65.01 50554'51"E L86 130.44 511'26'35"W L87 43.84 S05M2'56"W Les 106.16 S1329'35"W L89 49.46 S20'55'11"E L90 132.59 SD9'16'07'W L91 48.97 S1226'38°W L92 50.88 S53'01'06"W L93 109.27 S2015'33"W L94 78.86 S1 5'53'42"W L95 26.98 S2714'30'E L96 36.09 S13MO'35'E L97 6251 S3028'39"E L98 101.13 S3Y'42'43"E L99 189.69 543'59'41"W LIDO 80.49 578'55'00' L101 89.80 S5014'54'E L102 9281 $47'05'21"W L103 145.50 579'48'50"E L1 D4 61.18 53825'49"E L705 42.09 S2219'54"E Li 06 130.50 S2439'01"W L107 65.50 S2820'17'W L108 145.95 S1 0'09'50"E L109 171.52 S2555'23'E L110 75.53 519'44'19"E L111 69.17 S3605'18'W L112 166.53 S5011'42E L113 167.87 N3956'57E L114 59.14 S27'IW13"E L115 113.86 SD6'04'12'W L116 102.09 531'44'46° L117 38.41 S0934'39"E L118 116.81 S0636'40'E L119 44.80 SD659'03'E L120 29.60 55536'29"W L121 123.02 S29'02'59"E L122 71.59 N3224'02'E L123 5270 SQ2 W03"E L124 115.60 S1211'31'W L125 71.85 S36'49'54W L126 26.88 S5116'42"W L127 88.29 N08'38'28"W L128 215.42 SSB'42'11°W L129 25.00 588'4217"W L130 54.34 NOB12' 5'W L131 93.85 N2511'53"W L132 69.32 N52'49'04°W L133 45.82 N31'49'23"W L134 53.75 N36'3r38"E N L135 90.39 N2000'31"W 1-136 54.65 NBB59'41'W L137 88.39 N51'02'14"W L138 47.51 N46'04'53"W L139 121.90 N0218'05'E L140 91.46 N34'4422"W L141 16208 N1929'04"W L142 88.36 N76'19'27 W L143 8276 N12'02'42"W L144 75.05 S825r4O'E L145 3202 S77'5718'E L146 23.80 NBB'02'51'E L147 78.95 N071 2'43"W L148 69.43 N5058'30"W L149 59.87 N06'35'30"W L150 98.16 N2804'09"E L151 115.57 N68'03'0.5"W L152 74.47 N10'36'26'E L153 114.90 S79'45'58'E L154 71.07 N0724'13'E L155 54.59 N6836'53"W L156 103.88 N27'51'37W L157 111.85 N1306'36'W L155 78.98 N4926'15"W L159 8267 N3711'39°E L160 95.26 N42'00'01"W L161 41.75 N322224°W Li 62 80.16 N55'34'06"E LINE TABLE (CONTINUES) LINE LENGTH BEARING L163 29.08 N0224'43'E L164 49.10 N2120'5VW L165 54.50 N8251'03"W L166 45.66 N815W40"W L167 53.99 N0871-18' - L168 84.09 N79-03'1 3-E L169 29.00 N1838'49' L170 75.54 N1231'03'E L171 120.53 N63'11'14"W L172 40.88 N6724'25'W L173 135.99 N4252'49'W L174 129.44 N52'49'54'W L175 54.35 N3 40'W L176 32.84 N37'02'10"E L177 67.91 57206' "E L178 163.20 5563 '28' L179 69.59 53712'15 1-180 9218 563'05'58"E L181 74.48 56631'55" L152 116.49 N 95B' r L183 53.95 N0110' 4"E L104 46.36 N25'42'18' L185 74.78 N2321'55'E L186 71.01 N4918'56'W L187 81.27 N8301'39"W L1 B8 10283 N01'0Y49'E L169 148.48 N38'05'05'W L190 165.68 N4321'27"W L191 448.12 N6412'49"W L192 582.79 N51'07*10'W L193 31251 S57*49'36'W L194 713.55 N7620'09'W L195 54.11 NOI10-33' L196 125.70 N0111'18"E L197 86.23 N12W40"W L198 25210 N02'43'3B"W L199 135.85 N3744'26"W L200 328.22 N3820'57"W L201 148.17 N8655'1 4"W L202 75.78 N4755'56"W L203 225.10 N38'51'27'W L204 58.42 N18'49'52"W L205 221.50 N091r56'W L206 158.08 N053r22'W L207 50.88 N41'38'51"E L208 90.60 N4328'58"E L209 7&62 N2000'01'E L210 7205 N16'44'53"W L211 137.01 N03'48'54"E L212 41.58 N6120'20'E L213 29.33 S4905'01'E L214 194.65 512'47'51"E L215 160.15 S16'06'30"W L216 208.39 S120r28"W L217 109.50 513'45'06°E L218 41.10 S1606'13°W L219 157.01 S23'4r41"E L220 95.48 S50'44'OrE L221 44.90 S6059'56'E L222 53.07 N2000'01"E L223 51.76 $6959'59" L224 55.65 S04'08'29"W L225 7242 S551 1'48'E L226 58.70 N302558"E L227 139.91 N3915'46'E L228 104.59 N2458'25"E L229 83.26 N1929'59"E L230 61.06 N3519'19'E L231 131.61 N5459'59'W L232 56.26 N6028'35"E L233 76.06 S8352'34"E L234 15269 N4929'31' L235 144.31 N46'0r3O'E L236 25.90 S62'45'32' L237 77.43 58354'59"E L238 17.90 S1 8'45'05'E L239 56.30 S07'36'50"W L240 85.79 S2556'40"W L241 77.19 S6500'01"W L242 105.24 S33'08'43"W &c= 243 NORTH FRONT STREET WILMINGTON, NORTH CAROLINA 28401 TELEPHONE: (910) 251-6665 FAX: (910) 794-1154 NORTH CAROLINA FIRM LICENSE NUMBER: C-0342 LINE TABLE (CONTINUES) LINE LENGTH BEARING L243 93.99 531'50'36"W L244 113.49 556'49'55E L245 47.79 S35'00'01'W L246 119.40 S8725'1 3'W L247 157.44 S35'00'01"W L248 74.19 S13'42'55"W L249 70.19 N8932'46'W L250 88.34 S10-Ir35'W L251 180.81 S475rO7'E L252 80.71 S34'41'57'E L253 49.38 S2316'58"W L254 94.51 541'00'48"E L255 77.32 S2612'52"E L256 237.47 S12'42'07'E L257 10.38 NB000'01"E L258 135.59 N4225'45"E L259 129.02 N6315'03' L260 6255 N042r00" L261 59.57 N3W40'26' L262 46.22 N822r19'E L263 23.15 S35 '06" L264 78.89 50116'12E L265 171.18 S8911'03"E L266 83.67 N56'06'49"E L267 200.57 N23'01'34E L25B 76.02 N793rO4"E L269 85.55 N44'01'55' L270 105.69 N61'59'50"E L271 93.07 N4816'01° L272 35.73 S7620'4r L273 194.61 S10'0r32'W L274 73.23 N6032'47'W L275 83.44 S37'38'16'W L276 5219 N69'48'15"W L277 178.01 S41'4r15'W L278 53.95 S0303'1 9'W L279 90.68 S3032'1 4'W L280 88.02 5845 '33°W L281 86.23 S86.35'13'W L282 161.92 N81'06'07"W L283 131.58 S4526'52"W L284 130.36 S50'01'21"W L205 4265 SD620'40"W L286 80.68 S49'43'1 7"W L287 66.68 S0154'07'W L288 73.74 S2829'40"W L289 14.04 5482550"W L290 23.17 S64'44'07'W L291 70.92 N7812'14'W L292 326.80 54432'33"E L293 20.51 S451)72rW L294 82.14 N7611'55"W L295 71.21 S34'31'30'W L296 106.61 S54!34'1 3'W L297 54.69 54130'08"W L298 65.27 S53'0r50'W L299 133.39 S585r38"W L300 7239 S1826'05'E L301 84.74 57754'08"W L302 110.76 S4223'52'W L303 68.65 S2159'04'W L304 147.21 S6608'1 2'W L305 59.78 S3646'55'W L3D6 46.45 S13'02'05"W L307 115.65 S1455'58"E L308 95.42 521'4536"W ON 23.60 S122740'W L310 81.32 S20'33'21 "E L311 93.98 567'4122"W 1-312 64.09 N6117'12°W L313 55.18 S3952'58'W L314 47.38 S2224'03"W L315 39.92 S1715'58'E L316 54.56 S4620'07"E L317 146.18 S0735'35'W L318 5258 S7229'21'E L319 60.28 S3009'34E L320 80.78 S35'42'16"W L321 89.70 S8252'5rE 1-322 84.90 503*W08'W CONSERVATION EASEMENT SURVEY FOR WEYERHAEUSER REAL ESTATE DEVELOPMENT COMPANY PORTION OF ONSLOW 19 TRACT RICHLANDS TOWNSHIP - ONSLOW COUNTY - NORTH CAROLINA JULY 6, 2010 LINE TABLE (CONTINUES) LINE LENGTH BEARING L323 77.53 58416'39"E L324 54.04 S4459'59'E L325 72.47 S0236'02'W L326 53.98 S1359'04'E L327 9246 N883235 L328 29.81 N04'05'D9'E L329 4296 N5739'34"E L330 44.37 N4016'11"E L331 171.24 ND8103'55"E L332 72.37 N2617'32"W L333 44.60 N0620'01"W L334 60.75 N3839'37"E L335 64.81 N6914'15"E L336 47.88 N46'46'05"E L337 60.19 N17'38'2rE L338 22.40 N44'55'14"E L339 97.86 N4038'41"E L340 11.75 N3 4'18"W L341 57.05 N24'05'43"W L342 58.71 N0917'26'W 1-343 57.23 N03'05'29'W L344 43.55 N74'40'31'W L345 97.53 N18 5'18"E L346 36.10 N1 345'20"E L347 93.14 N5452'24"E L348 51.92 S8158' "E L349 114.68 N 458'54' L350 57.52 N781 3'36'E L351 59.64 N79V1'15" L352 36.49 S791)2'31"E L353 37.97 N71'39' 6'E L354 42.10 N861B'DB° LW5 35.18 N7822'25' L356 41.30 N7150' 0"E L357 42.95 N88'48'33'E L358 38.52 N64'09'58'E L359 57.73 N78'04'57E L360 39.99 N 89'16'03"E L361 40.40 N6421'14'E L362 55.00 N7131'04'E L363 44.82 N5111'20"E L364 203.36 S4452'33'E L365 218.36 S44'46'23'W L366 1220 S3604'13'W L367 19.15 S53'49'46'W L368 27.52 S10 '52'W L359 97.65 S33106'03'E L370 40.81 S48W05*E L371 13.43 S2823'14°E L372 51.92 SD8'46'24"E L373 20.63 S221 6'40'W L374 6207 19'44"W L375 9.05 S6624'15'W L376 56.74 S7928'47'W L377 11.66 N8334'34"W L378 55.31 N663755"W L379 85.31 S72'OW16'W ON 5266 N74'41'36°W L381 19.74 S75'44'1rW L382 19.74 51636'03"W L383 57.59 S1258'04"E L385 17.53 S65'00'08"W L386 27.70 N8900'28'W L387 12.89 S7211'48"W L388 12.89 S3436'21"W L389 24.87 S1548'37W L390 9.22 S2908'16"W L391 9.22 S55'4734W L392 48.82 S59'0713"W L393 159.87 N0904'31°W L394 89.01 S41'45'19'W L395 60.87 S12'41'46"W L396 86.94 5163754"W L397 80.31 SOO'32'34'E L398 45.56 S0231'33'E L399 128.71 S1 8'51'56"W L400 95.60 S4916'41"W L401 35.35 523'41'53"W L402 62.27 53251'22"W L403 124.06 S0322'01"W JOB NUMBER: 00910-0166 SCALE: 1" - 200' CAD NUMBER: VB101-O09100166 PIS: OEM PARTY CHERF: CB.MC.DW,AK CAD TECH: ACS FIELD BOO"AGE: W1239/16 DRAWING NUMBER: 2070-9e9 SHEET 9 OF 11 LINE TABLE (CONTINUES) E LENGTH BEARING 4 26. 25 51034'43"E 5 2&89 506'01'24"E j 6 43.32 53624'37W 7 64.44 537'31'35°W 8 842.35 576'05'52"W 9 52.88 S76V5'S2"W L 0 43.24 N35'04'11"W L411 16.24 N14'49'48W L412 20.31 N0352'46'W L413 26.82 N01 '06'59'W L414 52.11 N1 25'58"E L415 27.01 N3329'01"E L416 100.06 N1550'03"W L417 57.75 N3525'33"E L418 54.40 N66'48'O6"E L419 55.05 N2944'43°E L420 96.70 N435235°W L421 67.28 N2323'13°W L422 106.28 N37-WOO'E L423 92.56 N8 11'54"W L424 93.00 N1 826'05'W L425 33.82 N75'58'26'E L426 131.52 N04'4D'47"W L427 45.17 N45'00'01' L426 107.58 N4045'18'W L429 64.59 N1110'11"W L430 61.52 N3532'17'E L431 65.54 N0425'04"W L432 1.52 N5.21'01"W L433 13.12 N085725°W L434 165.49 NG8'5r25'W L435 155.98 N6931'07"E L436 42.85 55350'29'E L437 38.67 N432744"E L438 45.18 N652242°E L439 38.59 N32'45'29'E L440 70.74 N4530'34°E L441 52.58 N0158'33'W L442 76.63 N0738'1rE L443 56.39 N2r42'07'W L444 92.65 N0519'33"W L445 85.84 N5126'38"E L446 109.58 N0515'10"E L447 68.05 N705425'E L448 60.37 N3636'27'E L449 86.21 N7658'37"E L450 45.14 N66M2'21"E L451 22.57 N5330'42"E L452 19.19 N1751'29"W L453 45.33 N3556'39'W L454 96.33 N0723'39"W L455 79.78 N2732'11'E L456 118.65 N6120'27 E L457 86.50 NB6'05'30E L458 65.84 N7055'18"E L459 28.05 N88'44'00"E L460 56.49 N3052'53'E L461 106.79 N06'06'57°E L462 112.38 587'42'25"E L463 4200 N31-45-25-E L464 37.62 N7317'51"E L465 20.28 N451)7'27'E L466 707.25 N76'09'00°E L457 77.21 S42'30'42E L468 106.47 5441)1'13'W L469 196.28 55729'10"W L470 188.86 S73V4'44"W L471 65.21 511'4255"W L472 103.99 54024'00'W L473 86.66 53352'49"E L474 152.03 SD8'lS32'W 176.34 50811'09'E 40.20 S35V0'01'W 134.33 53718'50'E 184.89 S15'56'23'W I 58.52 t 534'36'15"W 13&03 51255'57'W 49.46 S3V36'39'E L482 1 95 .70 S12'53'49"W 122 .09 52700'39W W Lj LINE TABLE (CONTINUES) LINE LENGTH BEARING 1-484 204.45 S63'50'55 L485 59.05 S64V6'55'E L486 30.46 S26'48'11' 1-487 26.02 N7837'S5"W 1-488 205.41 S04'43'12"E L489 120.78 55255'48°W L490 61.42 5265V21'E L491 2.20 S58'01'39°W L492 68.21 S7O'I8'52°W L493 97.44 N4321'4rW L494 78.25 N24-IF22-W L495 246.37 N5817*44'W L496 123.44 N3327'41"W L497 63.04 NO '38'04"W L498 247.41 N0523' "E L499 322.40 N1453'14'E L5DO 161,84 N142650E L501 65.67 N2242'36"W L502 320.40 N0226'17'W L503 72.49 N1219'08'W L504 181.33 NDV44'5rE L505 57.10 N11TV21"W L505 156.45 N2615'33'E 4&34 N66 8'4rW 60.66 N4454'37 E 69.35 N6128'S8° L51 46.27 N7410'48"E g 132.77 N29'05'43E 397.99 N521)4'46°E 154.27 N5342'06'E 159.94 N19VW39"W L515 99.23 N5337'09"W L516 87.71 N1714'44"W L517 83.27 N0244'48°W L518 162.40 N0949'42"E L519 70.78 N25V1'45"E 1-520 200.03 N3527'46'E L521 116.59 N6429'51°E L522 8271 S26'40'54'E L523 213.51 S423r30°W 1-524 153.64 53030'59'W L525 195.09 50119'44'E L526 119.14 54410'53'E L527 74.15 53154'42"E L528 72.65 N40-17'04'E L529 275.34 N58'38'00°E L530 146.76 N6256'16"E L531 264.54 N00'30'59"W L532 187.15 N123V03"W 98.30 N4434'55'E 65.26 53852'18'E 8264 51610*57 E 73.24 51110'08'E p 54.51 SO642'42'W 181.17 SD031'57 E 97.28 51112'13'W L540 113.37 51112'13'00 L541 83.19 N70'3B'06"E L542 65.48 N055B'47 E L543 281.86 N2435'1C" L544 109.47 N33V8'35'E L545 69.72 SBO'48'24"E L546 366.13 51811'21"W L547 91.47 S8D12'36°E L548 220.31 N6959'20"E L549 67.78 N1525507W L550 50.25 N18'30'1WE L551 59.44 57529'28'E 1-552 92.15 51752'40'E L553 70.06 S89V4'37°E L554 255.15 N2820'49"E L555 141.04 N41'30'53'E L556 187.53 N43'37'42"E L557 159.54 N3153'40"E L550 84.89 N1010'53"E L559 82.72 N3834'10"W L560 10223 58118'00"W L561 48.17 N3759'56"W L562 79.45 N401 3'01"E L563 162.69 N2958'35°W LINE TABLE (CONTINUES) UNE LENGTH BEARING L564 129.33 579201"W L565 105.71 N6924'22"W 1-566 72.25 N1337'20'E 1-567 80.17 S7647'20'E L563 47.75 N1618'03"W L569 117.15 N10'34'21'E L570 47.60 58436'02"E L571 116.36 N3126'S0"E 1-572 8&55 N0151'11'W L573 63.52 N75'30'29' L574 101.15 N75'30'29'E L575 77.58 58359'39"E L576 105.33 7'37'E L577 26.85 S4338' 1"W L578 103.81 55119'25W L579 96.50 S4O°45'31"W L580 69.30 $30'06'21"W L581 109.50 S10'00'24"E L582 112.52 52739'5rE L553 106.90 45'51'E L554 155.92 S 54'37°E L585 51.42 53532'37 E L586 135.79 N43'58' 8'E L587 59.53 N55'09'55'E L588 174.28 NB9'00'43'E L589 87.48 58717'23" L590 46.65 N5658'39 L591 63.21 N64 *25'59"E L592 B8.64 N51'35'19"E L593 41.32 N5050'39"E L594 7&31 N1010'03'W L595 120.5,V N 20-56'38"W L596 221.131' S41'51'53"E L597 60.8x' 5171r32°W L598 75.10 S '30'42"W L599 49.58 S30'06'43°W L6DD 61.75 5611455"W L601 151.55 S72U7*31'W L602 229.21 57657'06"W 1-603 93.62 52850'19"E L804 53.87 53459'52°W L605 144.92 57358'02°W L506 155.25 58018'06"W L607 174.24 54418'59"W L608 237.61 5301)4'44"W L609 179.94 53354'33W L610 76.25 S33'04'04°W 1-611 99.26 5735993"E L612 20&67 5511)1'02°E L613 47.73 N5732'1 5"E L614 59.91 58932'51 L615 112.07 N26V6'36"E 1-616 145.77 N54'08'D6'E L617 95.62 N5712'54E L618 54.06 S51'43'25"E L619 67.07 S29'42'17'W L620 100.84 S49'02'14°W L621 150.04 S49'54'34W 1-622 34.38 54119'22°E L623 107.57 N6136'05°E L624 50.41 55353'46'E L625 127.23 SD411'32'W L626 51.07 S633r51°E L627 66.91 N37'41'00' L628 32.71 N4953'1 2"E L629 72.40 N76'34'21'E L630 166.48 51951'55"W L631 142.37 57013'34"E L632 8224 N57V8'17"E L633 37.06 S66'49'57"E L634 83.05 5021)7'S0'W L635 40.49 54353'07'E L836 56.06 S6927'2r L637 5&27 N64'36'03"E L638 136.34 N0018' 3° L639 100.02 N09'40'14° L640 74.84 N4819'07"E L641 156.64 N44'42'03°E L642 196.28 N16'46'06"E L643 104.55 N1935'40"E 243 NORTH FRONT STREET WILMINGTON, NORTH CAROLINA 28401 TELEPHONE: (910) 251-6665 FAX: (910) 794-1154 NORTH CAROLINA FIRM LICENSE NUMBER C-0342 LINE TABLE (CONTINUES) LINE LENGTH BEARING L644 144.75 N3 28'09°E L645 161.23 N3r46'19° L646 116.31 N47'45'15"E L647 31.32 N47'W15'E L648 250.10 S41'46`45°E L849 127.10 55058'10°W L650 185.15 54423'49W L651 135.77 5141)1'15°W L652 55.93 52520'08"W L653 86.31 51757'15°E L654 101,00 588M2'08'E L855 197.34 55839'49°E L656 112.87 55839'49'E L657 515.35 51125'42"W L658 167.97 N28V ' 8°W L659 84.09 1355'36'W L660 6&62 N1 234'38'W L681 97.89 563 8'11"W L662 210.08 N7 30'14°W L563 142.95 N731)4'03'W L664 39.56 S17MV3 °W L665 77.03 50823'31"W L666 83.91 S52-31'21 ' LS87 135.36 S43-46-31° 1-668 129.37 N7634°14°W L669 108.46 N 5'25'W L670 36.85 S43°40'44W L671 86.94 55616'53'W L672 131.98 50216'38°W L673 210.75 5511)4' 5"E L674 223.60 N89'42'36'E L675 106.38 N7156'46°E L676 223.50 N7678'53'E L677 137.66 511 '34"W L678 53.13' N585VO6"E L679 145.38 S76Ur57"W L680 75.64 520'4548"W L681 85.56 N4426'16'W L682 36.95 556'49'14'00 L693 62.56 52610'16'W L684 70.55 N8850'52°W L685 94.53 N59'5947W L686 13213 N6518'38"W L657 51.51 N5613'13°W L668 61.32 N4739' 9'W L639 10204 N36'49'S5"W L590 54.26 N0637'15°W L691 46.87 N '47'21'W L692 64.67 N1311'23°W L693 37.61 N201414'E L694 87.51 N63'1 5'55"W L695 59.52 N6759'39"W L696 83.62 N69'44'3 'W L697 92.35 N7513'O5'W L698 23.38 58415'55°W L699 66.19 Sir49'43'E L700 66.29 7'40'07' L701 66.44 54817'31"E L702 124.92 55335'23'E L703 51.75 5111)0'43"W L704 91.06 N801 8'20"W L705 43.66 54412'55°W L706 73.24 NBO'57*05°W L707 68.62 N20'41'20'E L708 56.50 N1112'44"W L709 105.31 N41'S0'19'W L710 85.13 N1957'20"W L711 72.28 N0528'37°W L712 108.12 N4738'03'W L713 19.24 58714'40"W L714 134.53 52351'41"W L715 76.10 N45°5SOB"W L716 135.05 N09'41'13'E L717 67.38 N64'1 2'09'W L718 150.90 N6115'42°W L719 0.00 53413'42"W L720 127.00 53413'24"W L721 60.18 N671,05"W L722 81.76 N17'41'45"E L723 53.02 N4835'14'W LINE TABLE (CONTINUES) LINE LENGTH BEARING L724 76.22 N0237'21"W L725 60913 N47 7'43'W L726 31.12 S873r54'W L727 70.14 N74V3'5 W L723 62.70 N5429'31°W L729 79.53 56725'33"W L730 12241 504'56'30"W L731 55.18 S11'23'48' L732 109.47 S11'05'58"E L733 170.03 SD2'Ir38' L734 121.45 S141)8'14"W L735 31.88 52125'41"E L736 100.48 735'45'E L737 131.81 S4229'1 O"E L738 82.47 S46'41'01"E L739 205.60 548'05'58' L740 92.94 S41V1' L741 96.33 53932'37"W L742 148.78 N4513'49'W L743 105.75 N45'49'40'W L744 139.34 N43'05'17'W L745 105.74 N4125'2rW L746 81.89 N3116'47W L747 110.17 N1658'09'W L743 176.51 N0722'51'E L749 172.54 N04'08'20'W L750 190.27 N1 1)5'50°W 1 24&47 S76'03'54"W 2 45.11 511183E 3 73.88 N7757'37 W 4 113.45 S55'4r24'W R 5 83.43 50628'22°W 6 146.01 S23'46'S5'E 7 77.85 S46'46'15"E L75a 93,00 574'40'43°W L759 130.12 N 39'13'05"W L760 146.27 N1 1'50'42"W L761 4&91 N7854'41'W L762 151.67 58427' 'W L763 68.78 S45V4'48°W L764 92.74 53032'47'W L765 91.72 54839'44"W L785 19&74 S6340'41"W L767 208.58 54712'31'W L768 17&16 562'07'20°W L769 98.75 N4723'48°W L770 258.02 N78'43'05°W LT71 31.94 N5520'41'E L772 103.47 N541O'04"E L773 26.25 N4531'30"E L774 23.55 N19'41'51"E L775 74.78 N3320'15"E L776 95.76 N7158'12°E L777 34.97 NB754'25'E L778 43.89 N3824'25°E L779 33.80 N7432'55'E L780 5217 N0439'1rW L781 82.22 N6751'44E L782 53.40 N49'45'32'E L783 38.51 N36'40'12" L784 98.91 N4830'54'E L785 34.44 N5445'02'E L786 27.24 N54'45'02'E L787 71.56 N0154'11"E L785 39.00 N28V4'4rW L789 128.66 N2058'43'W L790 35.31 N01'S5'41"E L791 80.80 N1353'34"W L792 78.48 N07'08'25"W L793 34.13 N09'42'2rE L794 33.42 N3123'01°W L795 72.68 N5750'32'W L796 51.34 N5615' 9"W L797 44.19 N7829'53"W L798 31.11 N7225'44"W L799 34.77 N5556'09"W 1-800 26.94 N66'4900W L801 49.46 N6353'30"W L802 48.27 N38'44'52W L803 63.78 NOB'46'36'W CONSERVATION EASEMENT SURVEY FOR WEYERHAEUSER REAL ESTATE DEVELOPMENT COMPANY PORTION OF ONSLOW 19 TRACT RICHLANDS TOWNSHIP - ONSLOW COUNTY- NORTH CAROLINA JULY 6, 2010 JOB NUMBER: 00910-0166 SCALE: 1" = 200' CAD NUMBER: 18101-009100166 PLS: DEM PARTY CHIEF: CB,MC,DWAK CAD TECH: ACS FIELD BOOK/PAGE: W1239/16 DRAWING NUMBER: 201 a-0"9 SHEET 10 OF 11 LINE TABLE (CONTINUES) LINE LENGTH BEARING L804 40.87 N463B'38"E L805 28.51 N0018'16'W L806 36.28 N1535'55"E L807 70.39 N30'22'22"W L808 89.89 N721,08"E L809 46.18 N2213'18'E L810 39.29 N46'21'50"E L811 39.79 N4319'55'E L812 43.62 N11'06'07"E L813 26.56 N57!WO1"E L814 15.47 N1434'07'E L815 60.39 N39'OB'38"E L816 47.09 NO130'34'E L817 39.88 N36W54"E L818 77.33 N3616'10"W L819 79.60 N12'4418"E L820 57.10 N53'29'10'E L821 52.45 N7273'01"E L822 127.44 SO 37'S5"E L823 928.75 5372729"E L824 51.84 T32'31'W L825 29.70 N8579°12"W L826 28.97 S81 '40'W L827 4219 N6572'39'W L820 72.20 568'42'24 W L829 115.70 $5638'05"W L830 62,95 S14'46'52'E L831 50.27 S0412'52'W L832 105.75 S1630'50'E L833 23.77 S3724'47"E L834 30.16 S0614'37"E L835 36.31 S26'06'39"E L836 44.51 S2118'27E L837 78.90 S1415'59'E L83B 28.76 S41'1 8`25'E L839 53.11 S157W44"E L840 60.51 S0279'42"E L541 48.91 S33'40'49'W L842 99.92 S4501'53'W L843 144.58 5050734"E L844 95.48 S30'43'28"W L845 63.97 S7934'47W L846 52.45 S7478'13°W L847 46.09 N6936'13'W L848 79,11 S54'20'28"W L849 30.00 S7936'32"W L850 31.91 SBB04'25"W L851 19.86 S3808'31'W L852 69.94 S55'26'25"W L053 21.30 S7338'55"W L854 42.34 SIB3B'OB"W L855 41.82 S8952'01'W L856 30.72 546'25'19"W L557 7.81 S5208'24W L858 21.56 S29'37'10"W L859 76.99 S4536'33"W L860 3202 SBO'11'37'W L861 49.94 S4106'40'W L862 335.18 N4100'53"W L863 151.78 N6934'21"E L864 185.97 NBT42'38"E L865 181.88 N6810'43' L866 128.86 N5409'43"E L867 137.91 N68'26'01"E L86B 154.75 N71'15'32"E L869 119.93 N81'25'07E L870 18214 N6430'28"E L871 146.67 N36'45'29"E L872 93.29 N36'45'29'E L873 106.21 NO409'39'W L874 21.29 N1135'21"W L875 58.83 N1 00737W L876 66.14 N0101'32E L877 80.73 N1231'53"W L878 14295 N050750'W L879 83.83 N2643'43"E LOBO 116.42 N1931'52"E L881 488.83 S37°2729"E 1862 64.76 S3644'29"E 1863 101.52 53833'49"W LINE TABLE (CONTINUES) LINE LENGTH BEARING L884 46.76 S28'41'03'W L885 41.20 500'21'22"E LBBB 11221 517'00'35"W L807 45.23 S88'04'22'W L888 56.04 S7410'49'W L889 58.77 S24'28'02"W L890 29.88 S3222'07°W 1-891 38.50 S241 8'29"W L892 28.20 N78'04'27'W L893 28.34 S11°45'46"W L894 67.02 5473559"W L895 64.52 N88'07°07E L896 41.37 S4912'06'E L897 10.03 S7618'23'E L898 33.16 S48'54'14"E L899 57.04 S73'4V39"E L900 30.68 S743W°DO'E L901 36.24 53932'09°E L902 39.54 N6105°48"E L903 50.95 S5O'W43"E L904 38.80 $463729"E L905 34.27 S27-IV22"E L906 2292 S40'52'02°E L907 6235 847°55'24E L908 42.26 S1706'OS"W L909 22.70 S1514'52"W L910 34.18 S2128'50"E L911 37.48 S5631'04°E L912 33.67 5622748"E L913 25.11 S5735'05"E L914 20.38 S743O'20'E L915 18.06 S87'25'34E L916 27.62 N8655'50'E L917 29.21 733'07' L918 40.94 N64'38'36"E L919 54.09 S40'40'15'E L920 2234 57343'41"E L921 56.24 D14'44"E L922 52.29 S0976'27"E L923 21.86 S4400'20'W L924 41.45 S7054'25'W L925 1298 N8914'41"W L926 39.27 N7711'43"W L927 31.56 N7903'15'W L928 3274 N2400'26"W L929 42.25 N75'43'56'W L930 57.13 N761722'W L931 1294 S68'58'28"W L932 37.19 N8106'28"W L933 32.98 N6827'13"W L934 46.95 N26'4B'16"W L935 17.19 N5502'18'W L936 39.87 N5555'55'W L937 18.03 N2350'37W L938 24.68 N5008'O6"W L939 30.97 N31'3712"W L940 29.13 N3924'38"W L941 51.24 N1135'47W L942 34.17 N291 9'56"W L943 40.78 N53°44'03"W L944 33.59 S3817'06"W L945 55.44 N3810'40"W L946 40.14 S42'24'08"W L947 80.59 N41'46'21"W L948 40.01 N6155'57W L949 34.58 S55'22'18'W L950 55.75 N27'22'28"W L951 43.14 56301'32"W L952 6236 556'45'19"W L953 43.74 N3951'42'W L954 98.15 S19°25'47W L955 77.03 N7833'17'W L956 39.33 S7639'10"W L957 34.96 S3114'12"W L958 67.35 S82'1 6'20'W L959 17.78 N24'29'2YW L960 27.91 S8832'44W L951 40.25 58313'19"W L962 29.49 N71°32'41"W L963 3241 S80'45'03 'W 1 ?? .. 1 I? y 5!? ' .1 C f ' . LINE TABLE (CONTINUES) LINE LENGTH BEARING L964 24.03 SBB'52'11'W L965 39.66 S1539'33"W L966 36.98 S570514°W L967 21.94 537'59'15"W L968 67.87 S24'41'21'E L969 25.35 S16'58'36"E L970 19.58 S3B09'48"E L971 70.78 542'03'49"E L972 8721 S580D'26"E L 773 70.79 S60'29'01'E L974 101.16 569'49'19' L975 7207 S7505'46'E L976 66.70 S 01'41"E L977 55.24 S6406'58'E L978 35.21 SO 51'44"E L979 43.25 S0004'37E L980 31.51 S87'49'5"W L981 73.76 502'28'25"E L982 6256 S6507'38'W L983 57.83 N6954'52"W L984 93.76 N8305'48'W L985 123.31 NO11715' L986 18.61 N6538'32'W L987 8216 539'25'1 'W L988 117.55 N8401'53"W L989 5260 N0300'03"E L990 81.39 N27'49'57"E L991 38.92 N0013'49'W L992 38.37 N70'49'34"W L993 41.94 N36'39'19'W L994 45.81 N7912'48"W L995 66.81 SiT48'19°W L996 64.51 N7218'01"W L997 66.73 NOT35' 3"E L996 18.42 N06'22'1 4"E L999 39.15 NO6'4O'34"E L1000 36.24 N12'24'19"E L1001 40.05 N07'O9'1VW L1002 34.27 N2613'04"W L1003 41,55 S7714'1 0"W L1004 16.87 S7415'12"W L1005 37.33 S8914'03'W L1006 29.26 S46'39'57"W L1007 24.73 S3752'54'W L1008 27.61 S4007'52'W L1DD9 15.95 S4835'40°W L1010 27.41 S3021'1B'W L1011 4282 55816'21"W L1012 74.92 N801 8'39"W L1013 69.04 S1352'21'E L1014 7247 58310'15"W L1015 23.64 N2932'31"W L1018 49.84 '51"W L1017 18.72 N8702'51'W 1-1018 43.75 N69'25'25"W L1019 23.67 N8513'30'W L1020 50.46 N7030'05"W L1021 49.68 S33'Or32'W L1022 17.78 S2235'30"E L1023 28.21 51034'59"E L1024 21.04 529-2 '35' L1025 36.51 S57'21'38"E L1026 33.57 S63'1 5'35"E L1027 1259 S5233'03"E L1028 25.16 S7618'22"E L1029 3203 S5438'51" L1030 44.88 S5031'44'E L1031 31.87 S2400'30"E L1032 43.77 S451719'E L1033 56.83 S531 7'24"E L1034 58.20 SO7'35'11"W Li 035 58.80 56246'04"E L1038 81.64 S463T1B"W L1037 64.10 S57'37'50'W L1038 46.54 S4444'00'W L1039 50.87 N7103'13"W L1040 60.77 N0105'38"W L1041 40.19 N26-20'1 9"E L1042 6283 N0639'20'E L1043 20.77 N2133'52"W 243 NORTH FRONT STREET WILMINGTON, NORTH CAROLINA 28401 TELEPHONE: (910) 251-6665 FAX: (910) 794-1154 NORTH CAROLINA FIRM LICENSE NUMBER: C-0342 LINE TABLE (CONTINUES) UNE LENGTH BEARING 17.29 N48'3447'W 45 18.52 N48 1YW 46 24.10 N37-01'39'W N 47 31.11 N 02'00'W 48 26.41 N72*W45'W 49 18.42 N732W20'W 50 33.14 S8519'OB'W L1051 103.10 N3838'36'W L1052 34.40 N1217'02'E 53 36.33 2314'OO' 54 2 3.09 N '49'45"W 55 48.61 N6352'28'W 56 211.18 N1110' 7E R 57 138.08 S7536'51'W 58 17.20 N6633'51"W 59 53.26 S6902'33"W 60 Lio 83.30 N3533'1 'W L1061 100.66 N1013'49"W L1062 58.60 N8236'28"E L1063 73.74 N1859'19'E L1064 74.34 S48'43'19"E L1065 48.53 N08'2745"E L1066 7263 N65 '41"E L1067 75.37 S5919'38'E L1058 62.96 S0615'01'W L1069 10.29 S140T18"W L1070 5227 S14'06'58"E L1071 19.34 S71'31'06"W Li 072 10.24 S4215'06"E L1073 30.31 501'24'19"E L1074 2244 11 5'33'W L1075 88.38 N4614'15'E L1076 2281 N4T46'19"E L1077 50.21 N5434'09" L1078 1272 N4353'28'E L1079 66.31 N300747' L10BO 48.33 N6815'36"E L1081 41.49 N27'08'28'E L1082 44.88 N221724W L1083 39.79 N35W25"E L1084 51.00 N0549'48°W L1085 57.19 N3630'47"E L1086 78.43 N4204'OB"E L1087 140.40 S5912'59"E L1088 69.90 S17'2716'W L1089 34.06 S11 T 4'W L1090 35.03 S13'49'52'W 1-1091 285 S1833'04'W L1092 44.14 S63'38'18"E L1093 27.87 S2628'57"E L1094 17.68 S7T41'46"E L1095 94.24 S6705'35E L1096 120.19 51945'31"W L1097 6&48 S8442'17'W L1098 47.57 S180732W L1099 20.21 S7532'17'W L11oo 84.67 N55'20'20"W L1101 21.06 N6915' "W L1102 28,96 S06'41'36"W L1103 73.05 55116'45"W L1104 39.49 S52'35'2YW L1105 81.09 588121'20"W L1106 108.95 N6326'52'W L1107 5209 N85'31'51"W L1108 19.82 S30'46'32"E L1109 34.86 N3131'08' L7110 71.70 N37"26"E 11111 65.96 N28'53'27E 11112 259X1 N1217'00' L1113 161.66 N04'4346'E L1114 130.90 N0336'16' L1115 149.12 NO67f32'E L1116 16&59 N3916'13"W L1117 65.19 N30'41'58"W 1-1118 181.03 N3723'00"W L1119 251.10 N39'21'40'W L1120 19.73 N875716"E L1121 328.61 5783557E L1122 101.97 S7903'06"E L1123 231.87 S2556'16'E LINE TABLE (CONTINUES) LINE LENGTH BEARING L1124 247.57 13'02°E L1125 54.33 52539'25 L1125 295.19 504'46'14° L1127 167.71 SO443'46'W L1128 215.22 535b4°W L1129 44.90 S2010'48°E L1130 219.68 S1613'39°W L1131 78.96 S8938'47"W L1132 125.54 S09'M47W L1133 260.02 N7834' 'W L1134 135.58 N153514" L1135 65.03 N13W29'E L1136 163.45 N3334'39'E L1137 116.29 NB4'4754'E L1138 113.83 S69'SD'55' L1139 84.41 54417'39' L1140 135.22 S1411'46°W L1141 85.72 51313'48' 11142 166.25 S16 5'03"E L1143 115.85 N805 '28"W 11144 279.77 N80'41'00'W 11145 57.26 N79'26'21'W CONSERVATION EASEMENT SURVEY FOR WEYERHAEUSER REAL ESTATE DEVELOPMENT COMPANY PORTION OF ONSLOW 19 TRACT RICHLANDS TOWNSHIP - ONSLOW COUNTY - NORTH CAROLINA JULY 6, 2010 JOB NUMBER: 00910-0166 SCALE: 1' = 200' CAD NUMBER: VB101-009100166 PLS: DEM PARTY CHEF: CB,MC,DWAK CAD TECH: ACS FIELD BOOK/PAGE: W1239/16 DRAWING NUMBER: Mir M169 SHEET 11 OF 11 STATE OF NORTH CAROLINA E COUNTY OF CNSLOW eaFFMtiW FVREST RVC,XAMS RENEW OFFICER OF ONSLOW COUNTY, CERTIFY TO THE BEST OF MY KNOWLEDGE AND BELIEF THE h-VY E `q M/PLAT TO WHICH THIS CERFICATION IS STATUUTO Y REQUIREMENTS FFORRRECORDNG. AFFIXED MEETS THE SHEET 2 SHEET 3 m n m z v Hu z LEGEND N/F - NOW/FORMERLY 1 DB = DEED BOOK MB = MAP BOOK PG - PAGE 0 = IRON ROD SET IRF0 = IRON ROD FOUND IPFO = IRON PIPE FOUND CMFO = CONCRETE MONUMENT FOUND ----- =PROPERTY LINE / SCALE: 1' = 1000' 6 560 1000 2000 3000 12.21 ACRES SHEET 5 SHEET 4 RENEW OFFICER DATE: FILED FOR REGISTRATION AT M O,CLOCK THIS OF AD _ IN PLAT CABINET ?SUDE Kttll? REGISTER OF DEEDS VICINITY MAP - NOT TO 2.97 ACRES 1.20 ACRES ? 0.42 A SURVEYOR'S NOTES: ? 1. BEARINGS BASED ON NC GRID (NAD 83) CORS 96. 45.15 ACRES 2. REFERENCES: DEED BOOK 2710 PAGE 916. DEED BOOK 516 PAGE 408. 3. SURVEYOR HAS MADE NO INVESTIGATION OR INDEPENDENT SEARCH FOR EASEMENTS OF RECORD, ENCUMBRANCES, RESTRICTIVE COVENANTS, OWNERSHIP, TITLE EVIDENCE, OR w ANY OTHER FACTS THAT AN ACCURATE AND CURRENT TITLE w SEARCH MAY DISCLOSE, a 4. SUBSURFACE AND ENVIRONMENTAL CONDITIONS WERE NOT EXAMINED OR CONSIDERED AS A PART OF THIS SURVEY. NO 59'67 N U STATEMENT IS THE NDERGROUND OR OVERHEAD IOOMER THIS 17.83 ACR THAT MAY Y AFF AFFECT THE HE USE USE OR DEVELOPMENT OF OF THIS TRACT. \? \ 5. SUBJECT TO ALL EASEMENTS, RIGHT OF WAYS, AND OR ENCUMBRANCES OF RECORD THAT MAY EFFECT THIS PROPERTY. SURVEYOR'S CERTIFICATION: SHEET 6 SHEET 7 \ 1, DAVID L JONES, JR, L-3872, CERTIFY THAT THIS PUT WAS DRAWN ?- V UNDER MY SUPERVISION FROM AN ACTUAL SURVEY MADE UNDER MY \ SUPERVISION FROM INFORMATION SHOWN IN DEED BOOKS AND (OR) MAPS REFERENCED ON THIS PLAT; THAT LINES NOT ACTUALLY r ?•? / SURVEYED APPEAR AS BROKEN LINES AND WERE PLOTTED FROM INFORMATION AS NOTED ON THE PLAT; THAT THE RATIO OF PRECISION AS CALCULATED BY LATITUDES AND DEPARTURES WAS GREATER THAN \ \? 1:10,000; THAT THE AREA IS COMPUTED BY COORDINATE METHOD; THAT THIS PLAT WAS PREPARED IN ACCORDANCE WITH G.S. 47-30 AS AMENDED. WTMESMY ORIGINAL SIGMTURE, LICENSE N BER, AND SEAL THIS TH Y OF-J)t e AD., SHEET 8 THIS SURVEY IS OF ANOTHER CATEGORY, SUCH AS THE RECOMBINATION OF EXISTING PARCELS, A COURT-ORDERED SURVEY, OR OTHER 1•???_ 3.00 ACRES EXCEPTION TO THE DEFINITION OF SUBDIVISION. MAD UNDER SUP FOLLLOWINGGINFORMATION WASE USED TO PERFORM THIS SURVEY. THE F- y j(_ it _ CLASS OF SURVEY., C - RURAL AND FARMLAND SURVEY POSITIONAL ACCURACY: 0.098 TYPE OF CPS FIELD PROCEDURE: OPUS OVERALL ACREAGE: 251.96 ACRES / DATES OF SURVEY. JANUARY 3, 2007 DATUM/EPOCH: NC GRID NAD53 CORS,46 PUBLISHED/FIXED-CONTROL USED,KENANSNLLE CORE ASTLE-HAYNECORS NEW BERN 2 CORS GEOID MODEU GEOID 03 COMBINED GRID FACTOR: 099899370-/ - _. UNITS; U.S. SURVEY FEET r ' 3 MY ORIGINAL SIGNATURE, LICENSE NUMBER; AND SEAL THIS - DAY OF ?AD'? r - ( °T per - DAVID JONES;-JR. PROFESSIONAL LAND SU R 9; 872 ; e ??'T?/T'??r CONSERVATION EASEMENT SURVEY JOB NUMBER: 00910-0166 &CF?'T?'? L FOR SCALE: 01 = 9100' 1.l M CAD NUMBER: V81D1-OD910D166 243 NORTH FRONT STREET WEYERHAEUSER REAL ESTATE PL9: DEM PARTY ? cB.MCJSAx WILMINGTON, NORTH CAROLINA 28401 DEVELOPMENT COMPANY CAD TECH- ACS TELEPHONE: (910) 251-6665 ' FAX: (910) 794-1154 PORTION OF ONSLOW 19 TRACT - 251.96 ACRES F>EID BOOK/PAGE: W1239/18 RICHLANDS TOWNSHIP - ONSLOW COUNTY - NORTH CAROLINA DRAWING NUMBER: 201 o-oss NORTH CAROLINA FIRM LICENSE NUMBER: C-0342 JULY 6, 2010 SHEET 1 OF ll 1 air z O Z Ll --7 N/F HOFFMAN FOREST MB 21 PG 140 i? i i 1 ?S INSET "A" SCALE 1"=20' LEGEND N/F - NOW/FORMERLY DB - DEED BOOK MB = MAP BOOK PG = PAGE • - IRON ROD SET IRF0 - IRON ROD FOUND IPF0 - IRON PIPE FOUND CMFE1 = CONCRETE MONUMENT FOUN .PROPERTY LINE SCALE: 1" = 200' 6 160 260 460 800 N/F NEYERHAEUSER REAL ESTATE DEVELOPMENT COMPANY MB 53 PAGE 3 INSET "A" NFM&CRMD 243 NORTH FRONT STREET WILMINGTON, NORTH CAROLINA 28401 TELEPHONE: (910) 251-6665 FAX: (910) 794-1154 NORTH CAROLINA FIRM LICENSE NUMBER: C-0342 NA- WYERHAEUSER REAL ESTATE DEVELOPMENT COMPANY DEED BOOK 2710 PAGE 916 N/1- REYERHAEUSER REAL ESTATE DEVELOPMENT COMPANY DEED BOOK 2710 PACE 916 IRS CONSERVATION EASEMENT SURVEY FOR WEYERHAEUSER REAL ESTATE DEVELOPMENT COMPANY PORTION OF ONSLOW 19 TRACT RICHLANDS TOWNSHIP - ONSLOW COUNTY- NORTH CAROLINA JULY 6, 2010 N/F HOFFMAN FOREST MB 21 PG 140 .I .I 70B NUMBER: DD910-0166 SCALE: 1' - 200' CAD NUMBER: VB1 01 -0091 D01 66 PIS: DEM PARTY CHIEF: CB.MC.DWAK CAD TECH: ACS FIELD BOOK/PAGE: W1239/16 DRAWING NUMBER: 20`0-069 SHEET 2 OF 11 N/F HOFFMAN FOREST MB 21 PG 140 _ 2d SOI ROAD IP IRS 3 o? rN 00 N T IRS SOVW33•W 15.70 IRS INSET "B" SCALE 1"=20' ,1 8< 1 N/F KEYERHAEUSER REAL ESTATE DELELOPMENT COMPANY DEED BOOK 2710 PACE 916 SEE INSET "B" MA1CHM Or - - ? ? _ SCALE: 1'= 200' Xl:M "-M 243 NORTH FRONT STREET D 160 260 400 600 WILMINGTON, NORTH CAROLINA 28401 TELEPHONE: (910) 251-6665 FAX: (910) 794-1154 NORTH CAROLINA FIRM LICENSE NUMBER: C-0342 HOFFMAN FOREST CONSERVATION EASEMENT SURVEY FOR WEYERHAEUSER REAL ESTATE DEVELOPMENT COMPANY PORTION OF ONSLOW 19 TRACT RICHLANDS TOWNSHIP - ONSLOW COUNTY- NORTH CAROLINA JULY 6, 2010 LEGEND N/F = NOW/FORMERLY DB - DEED BOOK MB - MAP BOOK PG - PAGE 0 = IRON RDD SET IRF0 = IRON ROD FOUND IPF0 - IRON PIPE FOUND CMFEI - CONCRETE MONUMENT FOUN ----- - PROPERTY LINE H 00??J m m g a o_ 2 ? L36 11.60 z y3 33.21' 4 33.26' J V ?? 70B NUMBER: 00910-0166 SCALE: 1' - 200' CAD NUMBER: VB101-009100166 PIS: DEM PARTY CHIEF: CB.MC.DW.AK CAD TECH: ACS FIELD BOOB/PAGE: W1239/18 DRAWING NUMBER: 2ma-0169 SHEET 3 OF 11 2 n I 2aas "?" 1 > r I _ i I. e I l m W r7 D 6 z O 2 LEGEND i N/F - NOW/FORMERLY DB - DEED BOOK MB - MAP BOOK PG = PAGE 0 = IRON ROD SET IRF0 -IRON ROD FOUND IPF0 - IRON PIPE FOUND CMFEI - CONCRETE MONUMENT FOUN --- -- - PROPERTY LINE N/F REYERHAEUSER REAL ESTATE DEVELOPMENT COMPANY DEED BOOK 2710 PAGE 916 M&Cn10 REBAR AND CAP N 406646.6200 E 2464178.2900 ELEV.45 .10' NO GRID NAD 83 N/F KEYERHAEUSER REAL ESTATE DEVELOPMENT COMPANY DEED BOOK 2710 PAGE 916 M&C N9J REBAR AND CAP N 406620.0690 E 2464896.7085 ELEV. 47.67 NO GRID NAD 83 N /F JEAN BRUCE WESTON DB 501 PG 74 MB5PG97 MATCMMM y J ? N CONSERVATION EASEMENT SURVEY JOB NUMBER: 00910-0166 /????''',TTT,???[///??'' j(t? FOR SCALE: 1' - 200' SCALE: I"= 200' - 1.1 iV.1116d CAD NUMBEST VB101-009100166 243 NORTH FRONT STREET WEYERHAEUSER REAL ESTATE Pas: DEM 6 100 200 460 Soo WILMINGTON, NORTH CAROLINA 28401 DEVELOPMENT COMPANY PARTY CIS'' CB.MC.DWAK TELEPHONE: (910) 251-6665 PORTION OF ONSLOW 19 TRACT CAD TECH: ACS FIELD BOOK/PAGE: W7239/16 FAX: (910) 794-1154 RICHLANDS TOWNSHIP - ONSLOW COUNTY - NORTH CAROLINA DBAWWG NUMBER: aD-D59 NORTH CAROLINA FIRM LICENSE NUMBER: C-0342 JULY 6, 2010 SHEET 4 OF 11 HOFFMAN FOREST i I i LEGEND `I I 7 I I I I I I N/F = NOW/FORMERLY DB - DEED BOOK MB - MAP BOOK PG - PAGE • = IRON ROD SET IRF0 = IRON ROD FOUND IPF0 - IRON PIPE FOUND CMFEI - CONCRETE MONUMENT FOUN - - - - - PROPERTY LINE MA1C?Il1lE G M1 KEYERHAEU REAL ESTATE DEVELOPMENT COMPANY DEED BOOK 2710 PAGE 916 S w 1 1 ? °a a 0 N HOFFMAN FOREST MB 21 PG 140 Fl ?I,W \ !6 ? A of ap ?a\ _ ,D s r P cb \ 5246' V5 1gti ?` 11111 - _ - - - - J N/F WEYERHAEUSER REAL ESTATE DEVELOPMENT COMPANY DEED BOOK 2710 PAGE 916 SCALE: 1" = 200' 6 160 260 460 Boo 243 NORTH FRONT STREET WILMINGTON, NORTH CAROLINA 28401 TELEPHONE: (910) 251-6665 FAX: (910) 794-1154 NORTH CAROLINA FIRM LICENSE NUMBER: C-0342 CONSERVATION EASEMENT SURVEY FOR WEYERHAEUSER REAL ESTATE DEVELOPMENT COMPANY PORTION OF ONSLOW 19 TRACT RICHLANDS TOWNSHIP - ONSLOW COUNTY - NORTH CAROLINA JULY 6, 2010 JOB NUMBER: 00910-0166 SCALE: 1' - 200' CAD NUMBER: VB101-009100168 PLB: DEM PARTY CHEEF: CB.MC,DWAK CAD TECH: ACS FMD BOOK/PAGE: W1239/16 DRAWING NUMBER: 20'" 169 SHEET 5 OF 11