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HomeMy WebLinkAbout20240175 Ver 1_Site Information Photos and Figures_202401247 Samuel Ashe Drive, Asheville, NC 28805 1 919-600-4790 1 greg@jenningsenv.com AGENT AUTHORIZATION FORM Project Name: Mouth of Hardin Creek Restoration Project Address/Location: Mouth of Hardin Creek south of Watauga High School Parcel ID 2910 8834 56000 (36.21219,-81.64937) The undersigned is the VProperty Owner Assigned a Easement Right -Of- Lease Holder F1 Representative Holder E Way Holder P and will be the applicant on the request for permit(s) and/or jurisdictional determination. I hereby authorize Jennings Environmental PLLC to act on my behalf and take all actions necessary for the processing, issuance, and acceptance of the permit or certification and any and all standard and special conditions attached. Additionally, I authorize the representative(s) of the permitting agency(s) to enter the property for the purpose of conducting activities associated with verification of the request for permit(s) and/or jurisdictional determination. I hereby certify that the information submitted in this document is true and accurate to the best of our knowledge. Name: Deron Geouque - County Manager Company Name (if applicable): Watauga County Mailing Address: 814 West King Street Phone Number: 828-265 Email Address: Derroon.Geougue ,watgov.org Signature: ��) ,� 1,"' Date: 8- 7- 2-023 Check if applicable ❑ The property owner has executed a binding agreement with the Natural Resources Conservation Service (NRCS) for this stream/wetland restoration project. The above is the assigned representative for the NRCS and is authorized to act on behalf of the NRCS and the property owner through a signed mutual agreement for the stream sabilization/restoration project. Jennings Environmental PLLC is licensed with the North Carolina Board of Examiners for Engineers and Surveyors and is authorized to practice engineering under the provisions of Chapter 89C and 55B of the General Statutes of North Carolina. License Number P-1932. Watauga County Auditor -fl! May 12, 2023 w 1:13,353 0 0.1 0.2 0 0.17 0.35 0.4 mi 0.7 km Watauga County Auditor 5/12/23, 12:30 PM PARID:2910883456000 WATAUGA COUNTY, Watauga County, NC 300 GO PIONEERS DR Parce ParlD Tax Year SITUS Addess City, State, Zip Unit # Unit Description NBHD Class Land Use Code Living Units CAMA Acres Zoning Map # Jan 1 Values Land Value. 16,349,500 Building Value 178,000 -------------------------- -------------------------- Appraisal Total 16,527,500 Exemptions or Exclusions 16,527,500 Land Deferred Value Taxable Total 0 _. Mailing Tax Year 2022 Sequence Number 0 Owner Number 1171255 Owner WATAUGA COUNTY Mailing Address 814 WEST KING ST SUITE 205 City, State, Zip BOONE NC 28607 Legai uescription Township 11 - NEW RIVER City Code Jurisdiction (Tax Code District) CO2 - BOONE Unit Desc Unit # Book P020 Page 078 Legal Desc 1 T-A WHS SITE P020/445 Deeded Acres 88.00 Sale Date Book Page Sale Price Grantor Grantee 18-MAR-08 020 445 tax.watgov.org/WataugaNC/Datalets/PrintDatalet.aspx?pin=2910883456000&gsp=SUMMARY&taxyear=2022&jur=095&ownseq=0&card=l&roll=REAL&State=I ... 1/2 � h } a' - ... ,, {.• e � 1r �?'�4+�3, �, �� . ,.' �'F fir",;. k• >`� .�.�f .' Id J. Ak Pl�e R. {' r '� � ' �'JS`I. �'1 it - }' — � — ��.+• ' S i r �.. �Ir if xf i'.y= •"r'_'.r..ti .#_ pc� I[�'..•._ .:.5 '..� �5w: a `i' _ i5 x%�, � _r?• ~ '� x7r-, �_. 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USGS 7.5 Minute Quad 5/12/2023, 12:13:07 PM 1:18,056 0 0.13 0.25 0.5 mi 0 0.2 0.4 0.8 km Copyright:© 2013 National Geographic Society, i-cubed USGS 2021 USGS USGS Hydrography Dataset Go Rio nos::: L i Y J yy0 1� ° Rd — 5/12/2023, 12:15:32 PM Waterbody - Large Scale Area - Large Scale Flume - Estuary Area of Complex Channels Foreshore Ice Mass Area to be Submerged Hazard Zone Lake Pond Baylnlet Inundation Area Playa Bridge Lock Chamber Reservoir Canal Ditch Rapids Swamp Marsh DamWeir SeaOcean U 0 1:4,514 0 0.03 0.06 0.12 mi 0 0.05 0.1 0.2 km State of North Carolina DOT, Esri, HERE, Garmin, INCREMENT P, USGS, EPA, USDA, USGS TNM - National Hydrography Dataset. Data Refreshed April, 2023. USGS 2021 USGS LiDAR Hillshade 5/12/2023, 12:17:02 PM 3DEP Elevation - Hillshade High : 255 Low: 0 1:4,514 0 0.03 0.06 0.12 mi 0 0.05 0.1 0.2 km State of North Carolina DOT, Esri, HERE, Garmin, INCREMENT P, USGS, EPA, USDA, USGS National Map 3D Elevation Program (3DEP). May 9, 2023. USGS 2021 USGS LiDAR Slope 5/12/2023, 12:18:03 PM 3DEP Elevation - Slope Map Red: Band 1 Green: Band 2 Blue: Band 3 1:4,514 0 0.03 0.06 0.12 mi 0 0.05 0.1 0.2 km State of North Carolina DOT, Esri, HERE, Garmin, INCREMENT P, USGS, EPA, USDA, USGS National Map 3D Elevation Program (3DEP). May 9, 2023. USGS 2021 USGS StreamStats Report Region ID: NC Workspace ID: NC20220113121957350000 Clicked Point (Latitude, Longitude): 36.21184,-81.64711 Time: 2022-01-13 07:20:19 -0500 .L f bone � 'q ,k Walachian f tor; i versit Basin Characteristics Parameter Code Parameter Description Value Unit DRNAREA Area that drains to a point on a stream 1.44 square miles PCTREG1 Percentage of drainage area located in Region 1 - Piedmont 0 percent / Ridge and Valley PCTREG2 Percentage of drainage area located in Region 2 - Blue 100 percent Ridge PCTREG3 Percentage of drainage area located in Region 3 - Sandhills 0 percent PCTREG4 Percentage of drainage area located in Region 4 - Coastal 0 percent Plains Parameter Code Parameter Description Value Unit PCTREG5 Percentage of drainage area located in Region 5 - Lower 0 percent Tifton Uplands BASINPERIM Perimeter of the drainage basin as defined in SIR 2004- 7.19 miles 5262 BSLDEM30FT Mean basin slope, based on slope percent grid 22.4 percent CSL10_85fm Change in elevation between points 10 and 85 percent of 161.13 feet length along main channel to basin divide divided by length per mi between points ft per mi ELEV Mean Basin Elevation 3330 feet ELEVMAX Maximum basin elevation 4420 feet 124H50Y Maximum 24-hour precipitation that occurs on average 9.28 inches once in 50 years LC01 BARE Percentage of area barren land, NLCD 2001 category 31 0 percent LC01 CRPHAY Percentage of cultivated crops and hay, classes 81 and 82, 5 percent from NLCD 2001 LC01 DEV Percentage of land -use from NLCD 2001 classes 21-24 52.5 percent LC01 FOREST Percentage of forest from NLCD 2001 classes 41-43 41.6 percent LC01 HERB Percentage of herbaceous upland from NLCD 2001 class 71 0.2 percent LC011MP Percent imperviousness of basin area 2001 NLCD 10.87 percent LC01SHRUB Percent of area covered by shrubland using 2001 NLCD 0.7 percent LC01 WATER Percentage of open water, class 11, from NLCD 2001 0 percent LC01 WETLND Percentage of wetlands, classes 90 and 95, from NLCD 0 percent 2001 LC06BARE Percent of area covered by barren rock using 2006 NLCD 0 percent LC06DEV Percentage of land -use from NLCD 2006 classes 21-24 52.9 percent LC06FOREST Percentage of forest from NLCD 2006 classes 41-43 41.6 percent LC06GRASS Percent of area covered by grassland/herbaceous using 0.2 percent 2006 NLCD LC061MP Percentage of impervious area determined from NLCD 2006 12.25 percent impervious dataset LC06PLANT Percent of area in cultivation using 2006 NLCD 4.6 percent LC06SHRUB Percent of area covered by shrubland using 2006 NLCD 0.7 percent LC06WATER Percent of open water, class 11, from NLCD 2006 0 percent Parameter Code Parameter Description Value Unit LC06WETLND Percent of area covered by wetland using 2006 NLCD 0 percent LC11 BARE Percentage of barren from NLCD 2011 class 31 0 percent LC1 1 CRPHAY Percentage of cultivated crops and hay, classes 81 and 82, 4.6 percent from NLCD 2011 LC11 DEV Percentage of developed (urban) land from NLCD 2011 53.1 percent classes 21-24 LC11 FOREST Percentage of forest from NLCD 2011 classes 41-43 41.4 percent LC11 GRASS Percent of area covered by grassland/herbaceous using 0.2 percent 2011 NLCD LC111MP Average percentage of impervious area determined from 16 percent NLCD 2011 impervious dataset LC11SHRUB Percent of area covered by shrubland using 2011 NLCD 0.7 percent LC11 WATER Percent of open water, class 11, from NLCD 2011 0 percent LC11 WETLND Percentage of wetlands, classes 90 and 95, from NLCD 0 percent 2011 LC92FOREST Percentage of forest from NLCD 1992 classes 41-43 52.7 percent LFPLENGTH Length of longest flow path 2.525 miles LU92BARE Percent of area covered by barren rock using 1992 NLCD 0 percent LU92DEV Percent of area covered by all densities of developed land 31.6 percent using 1992 NLCD LU92PLANT Percent of area in cultivation using 1992 NLCD 15.7 percent LU92WATER Percent of area covered by water using 1992 NLCD 0 percent LU92WETLN Percent of area covered by wetland using 1992 NLCD 0 percent MINBELEV Minimum basin elevation 3080 feet OUTLETELEV Elevation of the stream outlet in feet above NAVD88 3080 feet PRECIP Mean Annual Precipitation 56.1 inches PROTECTED Percent of area of protected Federal and State owned land 0 percent SSURGOA Percentage of area of Hydrologic Soil Type A from SSURGO 10.4 percent SSURGOB Percentage of area of Hydrologic Soil Type B from SSURGO 80.5 percent SSURGOC Percentage of area of Hydrologic Soil Type C from SSURGO 0 percent SSURGOD Percentage of area of Hydrologic Soil Type D from SSURGO 0 percent Peak -Flow Statistics Parameters [Peak Southeast US over 1 sgmi 2009 5158] Parameter Code Parameter Name Value Units Min Limit Max Limit DRNAREA Drainage Area 1.44 square miles 1 9000 PCTREG1 Percent Area in Region 1 0 percent 0 100 PCTREG2 Percent Area in Region 2 100 percent 0 100 PCTREG3 Percent Area in Region 3 0 percent 0 100 PCTREG4 Percent Area in Region 4 0 percent 0 100 PCTREG5 Percent Area in Region 5 0 percent 0 100 Peak -Flow Statistics Flow Report [Peak Southeast US over 1 sgmi 2009 51581 PII: Prediction Interval -Lower, Plu: Prediction Interval -Upper, ASEp: Average Standard Error of Prediction, SE: Standard Error (other -- see report) Statistic Value Unit PII Plu ASEp 50-percent AEP flood 146 ft"3/s 82.7 258 34.5 20-percent AEP flood 275 ft"3/s 157 483 34 10-percent AEP flood 377 ft"3/s 211 674 35.1 4-percent AEP flood 518 ft"3/s 279 962 37.5 2-percent AEP flood 622 ft"3/s 324 1190 39.6 1-percent AEP flood 746 ft"3/s 375 1490 41.9 0.5-percent AEP flood 856 ft"3/s 414 1770 44.3 0.2-percent AEP flood 1030 ft"3/s 474 2240 47.7 Peak -Flow Statistics Citations Weaver, J.C., Feaster, T.D., and Gotvald, A.J.,2009, Magnitude and frequency of rural floods in the Southeastern United States, through 2006—Volume 2, North Carolina: U.S. Geological Survey Scientific Investigations Report 2009-5158, 111 p. (http://pubs.usgs.gov/sir/2009/5158/) Bankfull Statistics Parameters [Appalachian Highlands D Bieger 2015] Parameter Code Parameter Name Value Units Min Limit Max Limit DRNAREA Drainage Area 1.44 square miles 0.07722 940.1535 Bankfull Statistics Parameters [Blue Ridge P Bieger 20151 Parameter Code Parameter Name DRNAREA Drainage Area Bankfull Statistics Parameters [USA Bieger 2015] Parameter Code Parameter Name DRNAREA Drainage Area Value Units Min Limit Max Limit 1.44 square miles 5.459454 125.999874 Value Units Min Limit Max Limit 1.44 square miles 0.07722 59927.7393 Bankfull Statistics Flow Report [Appalachian Highlands D Bieger 2015] Statistic Value Unit Bieger_D_channel_width 17.7 ft Bieger_D_channel_depth 1.24 ft Bieger_D_channel_cross_sectional_area 22.3 ft"2 Bankfull Statistics Disclaimers [Blue Ridge P Bieger 20151 One or more of the parameters is outside the suggested range. Estimates were extrapolated with unknown errors Bankfull Statistics Flow Report [Blue Ridge P Bieger 20151 Statistic Value Unit Bieger_P_channel_width 20.7 ft Bieger_P_channel_depth 1.23 ft Bieger_P_channel_cross_sectional_area 26.5 ft"2 Bankfull Statistics Flow Report [USA Bieger 2015] Statistic Value Unit Bieger-USA-channel-width 14.1 ft Bieger-USA-channel-depth 1.3 ft Bieger-USA-channel-cross-sectional-area 20.8 ft"2 Bankfull Statistics Flow Report [Area -Averaged] Statistic Value Unit Bieger_D_channel_width 17.7 ft Bieger_D_channel_depth 1.24 ft Statistic Value Unit Bieger_D_channel_cross_sectional_area 22.3 ft"2 Bieger_P_channel-width 20.7 ft Bieger_P_channel-depth 1.23 ft Bieger_P_channel_cross_sectional-area 26.5 ft"2 Bieger_USA_channeI_width 14.1 ft Bieger_USA_channel_depth 1.3 ft Bieger_USA_channeI_cross_sectional-area 20.8 ft"2 Bankfull Statistics Citations Bieger, Katrin; Rathjens, Hendrik; Allen, Peter M.; and Arnold, Jeffrey G.,2015, Development and Evaluation of Bankfull Hydraulic Geometry Relationships for the Physiographic Regions of the United States, Publications from USDA-ARS / UNL Faculty, 17p. (https://digitalcommons.uni.edu/usdaarsfacpub/1515? utm_source=digitalcommons.unl.edu%2Fusdaarsfacpub%2F1515&utm_medium=PDF&utm_carr USGS Data Disclaimer: Unless otherwise stated, all data, metadata and related materials are considered to satisfy the quality standards relative to the purpose for which the data were collected. Although these data and associated metadata have been reviewed for accuracy and completeness and approved for release by the U.S. Geological Survey (USGS), no warranty expressed or implied is made regarding the display or utility of the data for other purposes, nor on all computer systems, nor shall the act of distribution constitute any such warranty. USGS Software Disclaimer: This software has been approved for release by the U.S. Geological Survey (USGS). Although the software has been subjected to rigorous review, the USGS reserves the right to update the software as needed pursuant to further analysis and review. No warranty, expressed or implied, is made by the USGS or the U.S. Government as to the functionality of the software and related material nor shall the fact of release constitute any such warranty. Furthermore, the software is released on condition that neither the USGS nor the U.S. Government shall be held liable for any damages resulting from its authorized or unauthorized use. USGS Product Names Disclaimer: Any use of trade, firm, or product names is for descriptive purposes only and does not imply endorsement by the U.S. Government. Application Version: 4.6.2 StreamStats Services Version: 1.2.22 NSS Services Version: 2.1.2 USDA United States Department of Agriculture N RCS Natural Resources Conservation Service A product of the National Cooperative Soil Survey, a joint effort of the United States Department of Agriculture and other Federal agencies, State agencies including the Agricultural Experiment Stations, and local participants Custom Soil Resource Report for Watauga County, North Carolina Mouth of Hardin Creek June 16, 2023 Preface Soil surveys contain information that affects land use planning in survey areas. They highlight soil limitations that affect various land uses and provide information about the properties of the soils in the survey areas. Soil surveys are designed for many different users, including farmers, ranchers, foresters, agronomists, urban planners, community officials, engineers, developers, builders, and home buyers. Also, conservationists, teachers, students, and specialists in recreation, waste disposal, and pollution control can use the surveys to help them understand, protect, or enhance the environment. Various land use regulations of Federal, State, and local governments may impose special restrictions on land use or land treatment. Soil surveys identify soil properties that are used in making various land use or land treatment decisions. The information is intended to help the land users identify and reduce the effects of soil limitations on various land uses. The landowner or user is responsible for identifying and complying with existing laws and regulations. Although soil survey information can be used for general farm, local, and wider area planning, onsite investigation is needed to supplement this information in some cases. Examples include soil quality assessments (http://www.nres.usda.gov/wps/ portal/nres/main/soils/health/) and certain conservation and engineering applications. For more detailed information, contact your local USDA Service Center (https:Hoffices.sc.egov.usda.gov/locator/app?agency=nres) or your NRCS State Soil Scientist (http://www.nres.usda.gov/wps/portal/nres/detail/soils/contactus/? cid=nres142p2_053951). Great differences in soil properties can occur within short distances. Some soils are seasonally wet or subject to flooding. Some are too unstable to be used as a foundation for buildings or roads. Clayey or wet soils are poorly suited to use as septic tank absorption fields. A high water table makes a soil poorly suited to basements or underground installations. The National Cooperative Soil Survey is a joint effort of the United States Department of Agriculture and other Federal agencies, State agencies including the Agricultural Experiment Stations, and local agencies. The Natural Resources Conservation Service (NRCS) has leadership for the Federal part of the National Cooperative Soil Survey. Information about soils is updated periodically. Updated information is available through the NRCS Web Soil Survey, the site for official soil survey information. The U.S. Department of Agriculture (USDA) prohibits discrimination in all its programs and activities on the basis of race, color, national origin, age, disability, and where applicable, sex, marital status, familial status, parental status, religion, sexual orientation, genetic information, political beliefs, reprisal, or because all or a part of an individual's income is derived from any public assistance program. (Not all prohibited bases apply to all programs.) Persons with disabilities who require alternative means for communication of program information (Braille, large print, audiotape, etc.) should contact USDA's TARGET Center at (202) 720-2600 (voice and TDD). To file a complaint of discrimination, write to USDA, Director, Office of Civil Rights, 1400 Independence Avenue, S.W., Washington, D.C. 20250-9410 or call (800) 795-3272 (voice) or (202) 720-6382 (TDD). USDA is an equal opportunity provider and employer. Contents Preface.................................................................................................................... 2 SoilMap.................................................................................................................. 5 SoilMap................................................................................................................6 Legend..................................................................................................................7 MapUnit Legend.................................................................................................. 8 MapUnit Descriptions.......................................................................................... 8 Watauga County, North Carolina.................................................................... 10 EdD—Edneytown loam, 15 to 30 percent slopes........................................10 NkA—Nikwasi loam, 0 to 3 percent slopes, frequently flooded...................11 RoA—Rosman fine sandy loam, 0 to 3 percent slopes, occasionally flooded.................................................................................................. 12 W—Water....................................................................................................13 References............................................................................................................14 Soil Map The soil map section includes the soil map for the defined area of interest, a list of soil map units on the map and extent of each map unit, and cartographic symbols displayed on the map. Also presented are various metadata about data used to produce the map, and a description of each soil map unit. 068L00b OZ8L00b 09LLOOb 089L00b 0 Q U L = Q 0 CO w 0 '0 U) VJ E 0 U M „TT ,6£ oT8 096L00b 068L00b OZ8L00b z �o 09LLOOb Z m iD 069L00b Ob9L00b M „bb ,8£ oT8 W N >�W Z N N1 0 A _ W L>) > X �p�a5 g O g � N�Q M fh C � Q Q Q O O R Z iiijc M „TT,6£ oT8 089L00b MLOOb Ob9L00b z M �o N N y > O a) 0 y z N m o a) a) a) a) 3:c o U o o L N 52 o o.-_ a) m m o E °� a�i o U) w = y = U N E N U) > - > m O_ 0 — U a) Z (U O 0 O C N a) N a (n E U)-0 O O E a) o_ O_ m m E a) m m m O_ 3 U)) U o m U N O a) y a) = a) N E m y U) a) CJo O m a) '6 N z 0 U) E u)) o Q y ..- a) O C .�.-� Q (U (n O d a) m a) U) m Q N O 3: O '6 a) O `) N U) 0 E O W U N O O O N (U Q 0 U) Z 16 L 0- m a) N G O Q U m a) L y C U) m >. CL a) (U c U)-0 p (l) Q O 0 N O a) O 3 (n m 0 O_ �6 (j m E LL >+ a) (U a) p 6 a) — C> 7 U N O T a) O .� U O U O "�-' E a) O (V U N U) 0 >, m y Z ul s a) O a) a) O E a) m 7 w U O w O — 'O O)O y o_ N US E -0 a) m (U Q U m U 3 J> O N O-'E O m— g> a) a) -O C O iU E Qo m m m� z E - �Q � a`) n m a) o N 0-0 -E y o_ O E C y a) >+ a) O a) a) jU aaci a) (6 m a) m a) m E O O) N >' p 'O O y O_ a) U) a) U N (6 7 ,U) '6 N Q U) m ._ T O '6 O O_ O U) C m N y a) E o) O a) > 2 7 U U) a) .J 2i C (U N U .O U) Q m 'C O L O N E o_ m U) 0 C n E a) .� N '6 y E N O — (6 O C E m U O a : U a) "" '6 O> aa) m O a) m I� O '6 N L, p y O E (U 2) O N � a) 7 y y a) i U U) U O O_ a) 7 >+ U a) E y O) O O C O N N N N C N O m m N a) O O a) O O_ .a? a) C) (U O n� N —_ 0 7 —_ O O N °? m a) E miF H � S C O U W E= U U) a E u) U O_ 'O Q m L H o U) U) U)— 0 L O L H U. U) Q y d y R O (i U R L L Q Q >, 00 L d Q 0 J N CL m E a) .0. O m o O a o CL O U) (n > N L_ y O (n (n � o ° a) R m U 3) .a Q 0 R N R O C p O Z < a WR 4 R5 R fVn � F m W J y a aCL p y o o U) Q a U C > C C a) > > Q Q a w R 3 y O > a > ° w o ° o LU Q _ o o a co R R R w LL 3 3 o T a w > = `o E O a) o `o U) y Q 0 (n 0 0 o (n (n o m o R m U o U c7 c7 > R E J J Mn a) a O m m U) R a) U) U) a in U) O U) w a R ❑ ■ y0 ❑ a i/ ® �ap� <> { � y�p� "V `} ! o o }� �O y Q y ro Custom Soil Resource Report Map Unit Legend Map Unit Symbol Map Unit Name Acres in AOI Percent of AOI EdD Edneytown loam, 15 to 30 percent slopes 3.2 32.1 % NkA Nikwasi loam, 0 to 3 percent slopes, frequently flooded 4.7 46.3% RoA Rosman fine sandy loam, 0 to 3 percent slopes, occasionally flooded 2.1 20.9% W Water 0.1 0.7% Totals for Area of Interest 10.1 100.0% Map Unit Descriptions The map units delineated on the detailed soil maps in a soil survey represent the soils or miscellaneous areas in the survey area. The map unit descriptions, along with the maps, can be used to determine the composition and properties of a unit. A map unit delineation on a soil map represents an area dominated by one or more major kinds of soil or miscellaneous areas. A map unit is identified and named according to the taxonomic classification of the dominant soils. Within a taxonomic class there are precisely defined limits for the properties of the soils. On the landscape, however, the soils are natural phenomena, and they have the characteristic variability of all natural phenomena. Thus, the range of some observed properties may extend beyond the limits defined for a taxonomic class. Areas of soils of a single taxonomic class rarely, if ever, can be mapped without including areas of other taxonomic classes. Consequently, every map unit is made up of the soils or miscellaneous areas for which it is named and some minor components that belong to taxonomic classes other than those of the major soils. Most minor soils have properties similar to those of the dominant soil or soils in the map unit, and thus they do not affect use and management. These are called noncontrasting, or similar, components. They may or may not be mentioned in a particular map unit description. Other minor components, however, have properties and behavioral characteristics divergent enough to affect use or to require different management. These are called contrasting, or dissimilar, components. They generally are in small areas and could not be mapped separately because of the scale used. Some small areas of strongly contrasting soils or miscellaneous areas are identified by a special symbol on the maps. If included in the database for a given area, the contrasting minor components are identified in the map unit descriptions along with some characteristics of each. A few areas of minor components may not have been observed, and consequently they are not mentioned in the descriptions, especially where the pattern was so complex that it was impractical to make enough observations to identify all the soils and miscellaneous areas on the landscape. Custom Soil Resource Report The presence of minor components in a map unit in no way diminishes the usefulness or accuracy of the data. The objective of mapping is not to delineate pure taxonomic classes but rather to separate the landscape into landforms or landform segments that have similar use and management requirements. The delineation of such segments on the map provides sufficient information for the development of resource plans. If intensive use of small areas is planned, however, onsite investigation is needed to define and locate the soils and miscellaneous areas. An identifying symbol precedes the map unit name in the map unit descriptions. Each description includes general facts about the unit and gives important soil properties and qualities. Soils that have profiles that are almost alike make up a soil series. Except for differences in texture of the surface layer, all the soils of a series have major horizons that are similar in composition, thickness, and arrangement. Soils of one series can differ in texture of the surface layer, slope, stoniness, salinity, degree of erosion, and other characteristics that affect their use. On the basis of such differences, a soil series is divided into soil phases. Most of the areas shown on the detailed soil maps are phases of soil series. The name of a soil phase commonly indicates a feature that affects use or management. For example, Alpha silt loam, 0 to 2 percent slopes, is a phase of the Alpha series. Some map units are made up of two or more major soils or miscellaneous areas. These map units are complexes, associations, or undifferentiated groups. A complex consists of two or more soils or miscellaneous areas in such an intricate pattern or in such small areas that they cannot be shown separately on the maps. The pattern and proportion of the soils or miscellaneous areas are somewhat similar in all areas. Alpha -Beta complex, 0 to 6 percent slopes, is an example. An association is made up of two or more geographically associated soils or miscellaneous areas that are shown as one unit on the maps. Because of present or anticipated uses of the map units in the survey area, it was not considered practical or necessary to map the soils or miscellaneous areas separately. The pattern and relative proportion of the soils or miscellaneous areas are somewhat similar. Alpha -Beta association, 0 to 2 percent slopes, is an example. An undifferentiated group is made up of two or more soils or miscellaneous areas that could be mapped individually but are mapped as one unit because similar interpretations can be made for use and management. The pattern and proportion of the soils or miscellaneous areas in a mapped area are not uniform. An area can be made up of only one of the major soils or miscellaneous areas, or it can be made up of all of them. Alpha and Beta soils, 0 to 2 percent slopes, is an example. Some surveys include miscellaneous areas. Such areas have little or no soil material and support little or no vegetation. Rock outcrop is an example. Custom Soil Resource Report Watauga County, North Carolina EdD—Edneytown loam, 15 to 30 percent slopes Map Unit Setting National map unit symbol: ks8m Elevation: 1,200 to 3,000 feet Mean annual precipitation: 60 to 80 inches Mean annual air temperature: 46 to 57 degrees F Frost -free period: 124 to 176 days Farmland classification: Farmland of local importance Map Unit Composition Edneytown and similar soils: 85 percent Estimates are based on observations, descriptions, and transects of the mapunit. Description of Edneytown Setting Landform: Ridges, mountain slopes Landform position (two-dimensional): Summit, backslope Landform position (three-dimensional): Upper third of mountainflank, side slope Down -slope shape: Convex Across -slope shape: Linear Parent material: Residuum weathered from igneous and metamorphic rock Typical profile A - 0 to 5 inches: loam Bt - 5 to 21 inches: clay loam BC - 21 to 29 inches: fine sandy loam C - 29 to 80 inches: sandy loam Properties and qualities Slope: 15 to 30 percent Depth to restrictive feature: More than 80 inches Drainage class: Well drained Runoff class: High Capacity of the most limiting layer to transmit water (Ksat): Moderately high to high (0.57 to 1.98 in/hr) Depth to water table: More than 80 inches Frequency of flooding: None Frequency of ponding: None Available water supply, 0 to 60 inches: Moderate (about 6.9 inches) Interpretive groups Land capability classification (irrigated): None specified Land capability classification (nonirrigated): 4e Hydrologic Soil Group: B Ecological site: F130BY004WV - Mesic Residuum Warm Aspect Hydric soil rating: No 10 Custom Soil Resource Report NkA—Nikwasi loam, 0 to 3 percent slopes, frequently flooded Map Unit Setting National map unit symbol: ks75 Elevation: 2,000 to 2,650 feet Mean annual precipitation: 45 to 70 inches Mean annual air temperature: 46 to 57 degrees F Frost -free period: 116 to 170 days Farmland classification: Not prime farmland Map Unit Composition Nikwasi, frequently flooded, and similar soils: 70 percent Nikwasi, undrained, and similar soils: 10 percent Estimates are based on observations, descriptions, and transects of the mapunit. Description of Nikwasi, Frequently Flooded Setting Landform: Depressions on flood plains Down -slope shape: Concave, linear Across -slope shape: Concave Parent material: Loamy alluvium over sandy and gravelly alluvium Typical profile A - 0 to 26 inches: fine sandy loam Cg - 26 to 80 inches: extremely gravelly coarse sand Properties and qualities Slope: 0 to 3 percent Depth to restrictive feature: 20 to 40 inches to strongly contrasting textural stratification Drainage class: Very poorly drained Runoff class: Negligible Capacity of the most limiting layer to transmit water (Ksat): High (1.98 to 5.95 in/hr) Depth to water table: About 0 to 12 inches Frequency of flooding: NoneFrequent Frequency of ponding: Occasional Available water supply, 0 to 60 inches: Low (about 4.4 inches) Interpretive groups Land capability classification (irrigated): None specified Land capability classification (nonirrigated): 4w Hydrologic Soil Group: A/D Ecological site: F130BY011VVV - Hydric Floodplains Hydric soil rating: Yes Description of Nikwasi, Undrained Setting Landform: Depressions on flood plains Down -slope shape: Concave, linear 11 Custom Soil Resource Report Across -slope shape: Concave Parent material: Loamy alluvium over sandy and gravelly alluvium Typical profile A - 0 to 26 inches: fine sandy loam Cg - 26 to 80 inches: extremely gravelly coarse sand Properties and qualities Slope: 0 to 3 percent Depth to restrictive feature: 20 to 40 inches to strongly contrasting textural stratification Drainage class: Very poorly drained Runoff class: Negligible Capacity of the most limiting layer to transmit water (Ksat): High (1.98 to 5.95 in/hr) Depth to water table: About 0 to 12 inches Frequency of flooding: NoneFrequent Frequency of ponding: Occasional Available water supply, 0 to 60 inches: Low (about 4.4 inches) Interpretive groups Land capability classification (irrigated): None specified Land capability classification (nonirrigated): 7w Hydrologic Soil Group: A/D Ecological site: F130BY011VVV - Hydric Floodplains Hydric soil rating: Yes RoA—Rosman fine sandy loam, 0 to 3 percent slopes, occasionally flooded Map Unit Setting National map unit symbol: ks72 Elevation: 1,690 to 2,590 feet Mean annual precipitation: 50 to 58 inches Mean annual air temperature: 46 to 57 degrees F Frost -free period: 116 to 170 days Farmland classification: All areas are prime farmland Map Unit Composition Rosman, occasionally flooded, and similar soils: 80 percent Minor components: 5 percent Estimates are based on observations, descriptions, and transects of the mapunit. Description of Rosman, Occasionally Flooded Setting Landform: Flood plains Landform position (three-dimensional): Mountainbase Down -slope shape: Linear Across -slope shape: Linear Parent material: Loamy alluvium 12 Custom Soil Resource Report Typical profile Ap - 0 to 10 inches: fine sandy loam Bw - 10 to 59 inches: fine sandy loam C - 59 to 80 inches: fine sandy loam Properties and qualities Slope: 0 to 3 percent Depth to restrictive feature: More than 80 inches Drainage class: Well drained Runoff class: Very low Capacity of the most limiting layer to transmit water (Ksat): High (1.98 to 5.95 in/hr) Depth to water table: About 42 to 60 inches Frequency of flooding: Occasional Frequency of ponding: None Available water supply, 0 to 60 inches: Moderate (about 8.5 inches) Interpretive groups Land capability classification (irrigated): None specified Land capability classification (nonirrigated): 2w Hydrologic Soil Group: A Ecological site: F130BY012WV - Non-Hydric Flood plains Hydric soil rating: No Minor Components Toxaway, undrained Percent of map unit. 5 percent Landform: Depressions on flood plains Landform position (three-dimensional): Mountainbase Down -slope shape: Concave, linear Across -slope shape: Concave, linear Hydric soil rating: Yes ViTAMY 'i Map Unit Composition Water: 100 percent Estimates are based on observations, descriptions, and transects of the mapunit. Description of Water Interpretive groups Land capability classification (irrigated): None specified Land capability classification (nonirrigated): 8w Hydric soil rating: No 13 References American Association of State Highway and Transportation Officials (AASHTO). 2004. Standard specifications for transportation materials and methods of sampling and testing. 24th edition. American Society for Testing and Materials (ASTM). 2005. Standard classification of soils for engineering purposes. ASTM Standard D2487-00. Cowardin, L.M., V. Carter, F.C. Golet, and E.T. LaRoe. 1979. Classification of wetlands and deep -water habitats of the United States. U.S. Fish and Wildlife Service FWS/OBS-79/31. Federal Register. July 13, 1994. Changes in hydric soils of the United States. Federal Register. September 18, 2002. Hydric soils of the United States. Hurt, G.W., and L.M. Vasilas, editors. Version 6.0, 2006. Field indicators of hydric soils in the United States. National Research Council. 1995. Wetlands: Characteristics and boundaries. Soil Survey Division Staff. 1993. Soil survey manual. Soil Conservation Service. U.S. Department of Agriculture Handbook 18. http://www.nres.usda.gov/wps/portal/ n res/d eta i I/n ati o n a I/s o i Is/?cid = n res 142 p2_0 54262 Soil Survey Staff. 1999. Soil taxonomy: A basic system of soil classification for making and interpreting soil surveys. 2nd edition. Natural Resources Conservation Service, U.S. Department of Agriculture Handbook 436. http:// www. nres. usda.gov/wps/portal/nres/detail/national/soils/?cid=nres142p2_053577 Soil Survey Staff. 2010. Keys to soil taxonomy. 11th edition. U.S. Department of Agriculture, Natural Resources Conservation Service. http:// www. nres. usda.gov/wps/portal/nres/detail/national/soils/?cid=nres142p2_053580 Tiner, R.W., Jr. 1985. Wetlands of Delaware. U.S. Fish and Wildlife Service and Delaware Department of Natural Resources and Environmental Control, Wetlands Section. United States Army Corps of Engineers, Environmental Laboratory. 1987. Corps of Engineers wetlands delineation manual. Waterways Experiment Station Technical Report Y-87-1. United States Department of Agriculture, Natural Resources Conservation Service. National forestry manual. http://www.nres.usda.gov/wps/portal/nres/detail/soils/ home/?cid=nres142p2_053374 United States Department of Agriculture, Natural Resources Conservation Service. National range and pasture handbook. http://www.nres.usda.gov/wps/portal/nres/ detail/national/landuse/rangepastu re/?cid=stelprdb1043084 14 Custom Soil Resource Report United States Department of Agriculture, Natural Resources Conservation Service. National soil survey handbook, title 430-VI. http://www.nres.usda.gov/wps/portal/ n res/d eta i I/so i Is/scie ntists/?cid=n res 142 p2_054242 United States Department of Agriculture, Natural Resources Conservation Service. 2006. Land resource regions and major land resource areas of the United States, the Caribbean, and the Pacific Basin. U.S. Department of Agriculture Handbook 296. http://www.nres.usda.gov/wps/portal/nres/detail/national/soils/? cid = n res 142 p2_05 3624 United States Department of Agriculture, Soil Conservation Service. 1961. Land capability classification. U.S. Department of Agriculture Handbook 210. http:H www.nrcs.usda.gov/lnternet/FSE—DOCUMENTS/nrcsl 42p2_052290. pdf 15 Delineation of Wetlands and Waters Mouth of Hardin Creek Restoration Project Watauga County, North Carolina November 27, 2023 Prepared by: Jennings Environmental PLLC Asheville, NC Jennings Environmental PLLC is licensed with the North Carolina Board of Examiners for Engineers and Surveyors and is authorized to practice engineering under the provisions of Chapter 89C and 55B of the General Statutes of North Carolina. License Number P-1932. Jennings Environmental PLLC Delineation of Wetlands and Waters Mouth of Hardin Creek Restoration Project On September 14-15, 2023, a field evaluation of the project area for wetlands and streams was conducted by Jennings Environmental. Eight areas of wetlands and 4 streams were identified (see Wetland and Waters Map, Appendix C). The wetland areas have indicators of hydrophytic vegetation, hydric soils, and wetland hydrology per the Regional Supplement to the Corps of Engineers Wetland Delineation Manual: Eastern Mountains and Piedmont Region, Version 2.0 (Corps Regional Wetland Manual). The streams have several physical indicators of ordinary high mark (OHWM); presence of aquatic macro -invertebrates and fish; and observed flows. The U.S. Army Corps of Engineers defines a wetland as an area that is inundated or saturated by surface or ground water at a frequency and duration sufficient to support and that under normal circumstances do support a prevalence of vegetation typically adapted for life in saturated soil conditions. Wetlands at the site were identified following the methodology described in the Corps Regional Wetland Manual. Using this methodology wetlands are identified based on a three -factor approach involving evaluation of indicators of hydrophytic vegetation, hydric soils, and wetland hydrology. Wetland hydrology indicators provide evidence that a site has a continuing wetland hydrologic regime. These indicators confirm that there are regular episodes of inundation or soil saturation. Hydrophytic vegetation is a community of macrophytes that occur in areas where inundation or soil saturation is either permanent or of sufficient frequency and duration to influence occurrence of this plant community. Hydrophytic vegetation is present when the plant community is dominated by species that require or can tolerate prolong inundation or soil saturation during the growing season. Hydric soils are soils that have formed under conditions of saturation, flooding, or ponding long enough during the growing season to develop anaerobic conditions in the upper parts of the soil column. Saturation or inundation, when combined with microbial activity in the soil, causes the depletion of oxygen. This anaerobiosis promotes biogeochemical processes, such as the accumulation of organic matter and the reduction, translocation, or accumulation of iron and other reducible elements. The streams in the project area are an unnamed tributary (UT) of the South Fork New River locally called Hardin Creek, UTs of Hardin Creek, and the South Fork New River. The South Fork New River and Hardin Creek are depicted as solid blue lines on the U.S. Geological Survey 7.5 minute Boone, NC quadrangle map and the most current Natural Resource Conservation Service Soil Survey for Watauga County. Solid blue line features on these mapping conventions typically represent perennial streams. The UTs flow into Hardin Creek, which flows into the South Fork New River, and then flows into the New River, a traditional navigable water and navigable waters under Section 10 of the Rivers and Harbors Act. Historically the floodplains along Hardin Creek at the site had been used for pasture and growing crops. In the 1980s agricultural use at the site ended and during the last 35 years these areas have naturalized. A sewer line and a greenway trail is present in the project area. The Delineation of Wetlands and Waters— Mouth of Hardin Creek Restoration Project Jennings Environmental PLLC wetlands are well established with vegetation cover of mature tree, shrub, herbaceous, and vine species. Adjacent upland areas are also covered with mature vegetation. Summary of Existing Aquatic Features* Type Name Coordinates Size acres liner feet South Fork 36.21198 50 If New River -81.64711 36.21199 Hardin Creek 3,377 If Stream -81.64935 36.21374 UT1 342 If -81.65094 Wetland Connection / 36.21390 Surface Conveyance to UT2 256 If -81.65123 Stream W1 36.21150 0.027 ac Adjoins / Ephemeral -81.64754 W2 36.21116 0.029 ac Abuts / Intermittent -81.64826 W3 36.21177 1.321 ac Abuts / Perennial -81.64935 W4 36.21191 0.098 ac Abuts / Perennial -81.64911 Wetland 36.21300 W5 0.131 ac Abuts /Intermittent -81.65011 W6 36.21389 0.799 ac Abuts / Perennial -81.65108 W7 36.21469 0.055 ac Abuts / Perennial -81.65211 W8 36.21523 0.174 ac Abuts / Intermittent -81.65276 * These aquatic features are assumed jurisdictional/regulated by the US Army Corps of Engineers (Corps). The purpose of this evalaution is to make an effective analysis of the presence of waters and wetlands within the project area in order to determine proposed impacts to these aquatic features for planning and permitting. Jennings Environmental is not requesting the Corps to make the appropriate jurisdictional determination of these aquatic features under their current regulatory law/guidance. Delineation of Wetlands and Waters— Mouth of Hardin Creek Restoration Project Jennings Environmental PLLC Ubserved Physical Indicators of UHWM in Streams Break in slope Change in sediment texture Change in vegetation density Natural line impressed on the bank Change in soil character Shelving Vegetation absent Leaf litter washed away Sediment deposition and sorting Water staining Presence of debris Wrack lines Scour Observed and predicted flow events Observed Wetland Indicators Wetland Hydrology Surface water Saturation Sediment deposits Presence of reduced iron Water -stained leaves Oxidized rhizospheres on living roots Drainage pattern Crayfish burrows Geomorphic position Microtopographic relief Surface soil cracks Hydric Soils Depleted matrix Hydrophytic Vegetation acer rubrum juncus spp. salix nigra phalaris arundinacea sambucus canadensis betula nigra rhododendron maximum persicaria perfoliata eupatorium fistulsum betula lenta fraxinus pennsylvanica lobelia cardinalis persicara sagttatum sparganium americanum bidens frondosa mentha arvensis alnus serrulata Impatiens capensis conrnus amomum acernegundo leersia oryzoides osmunda spectabilis scirpus cyperinus carpinus caroliniana viola sororia helianthus grosseserratus peltandra virginica saururus cernuss vernonia noveboracensis symplocarpus foetidus Delineation of Wetlands and Waters— Mouth of Hardin Creek Restoration Project 3 Jennings Environmental PLLC APPENDIX A. Photo Log Delineation of Wetlands and Waters— Mouth of Hardin Creek Restoration Project Jennings Environmental PLLC Photo 1: Typical Wetland Soils (W3) Photo 3: Hardin Creek Photo 2: Typical Upland Soils in Floodplain Delineation of Wetlands and Waters— Mouth of Hardin Creek Restoration Project Photo 4: Hardin Creek 70 lli 17 t^-� 'a r -.77� :�s a. J'Pl.`.Yr``=,'h� , ?-7 t. i�`�a�� �r+: L5.7 r�l'�• m a Ti.Gd.�." N�.fz �` s a Jennings Environmental PLLC Photo 9: Wetland W3 Photo 11: Wetland W3 Delineation of Wetlands and Waters— Mouth of Hardin Creek Restoration Project Photo 10: Wetland W3 Photo 12: Wetland W4 Jennings Environmental PLLC Photo 13: Wetland W5 Photo 14: Wetland W6 Photo 15: Wetland W6 Delineation of Wetlands and Waters— Mouth of Hardin Creek Restoration Project Jennings Environmental PLLC APPENDIX B. Wetland Determination Data Sheets Delineation of Wetlands and Waters— Mouth of Hardin Creek Restoration Project Jennings Environmental PLLC U.S. Army Corps of Engineers OMB Control #: 0710-0024, Ezp:1113012024 WETLAND DETERMINATION DATA SHEET — Eastern Mountains and Piedmont Region Requirement Control Symbol EXEMPT., See ERDC/EL TR-12-9; the proponent agency is CECW-CO-R (Authority: AR 335-15, paragraph 5-2a) Project/Site: Mouth of Hardin Creek Restoration City/County: Boone, Watauga County Sampling Date: 9/14-15/23 Applicant/Owner: Jennings Environmental, PLLC State: NC Sampling Point: Upland Investigator(s): D. Brown Section, Township, Range: N/A Landform (hillside, terrace, etc.): Floodplain bench Local relief (concave, convex, none): None Slope (%): 1-3% Subregion (LRR or MLRA): LRR N Lat: 36.21181 Long:-81.64757 Datum: NAD 1983 Soil Map Unit Name: Rosman (RoA) and Nikwasi (NkA) NWI classification: N/A Are climatic / hydrologic conditions on the site typical for this time of year? Yes X No (If no, explain in Remarks.) Are Vegetation X , Soil X or Hydrology X significantly disturbed? Are "Normal Circumstances" present? Yes X No Are Vegetation , Soil or Hydrology naturally problematic? (If needed, explain any answers in Remarks.) SUMMARY OF FINDINGS — Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes X No Is the Sampled Area Hydric Soil Present? Yes_ No X within a Wetland? Yes_ No X Wetland Hydrology Present? Yes X No Remarks: Pre-1990's the site was in agricutural use (pasture & crops). During the last 30-35 years the site has naturlized. Sewerline construction & greenway development have disturbed the hydrology, soils & vegetation. Reed canary grass (phalaris arundinacea) is a dominant herbaceous species in open areas. HYDROLOGY Wetland Hydrology Indicators: Secondary Indicators (minimum of two required) Primary Indicators (minimum of one is required: check all that apply) _Surface Soil Cracks (136) _Surface Water (Al) _True Aquatic Plants (1314) _Sparsely Vegetated Concave Surface (138) _High Water Table (A2) _Hydrogen Sulfide Odor (Cl) _Drainage Patterns (1310) _Saturation (A3) _Oxidized Rhizospheres on Living Roots (C3) —Moss Trim Lines (1316) _Water Marks (131) _Presence of Reduced Iron (C4) _Dry -Season Water Table (C2) X Sediment Deposits (132) _Recent Iron Reduction in Tilled Soils (C6) _Crayfish Burrows (C8) _ Drift Deposits (133) _Thin Muck Surface (C7) _Saturation Visible on Aerial Imagery (C9) _Algal Mat or Crust (134) _Other (Explain in Remarks) _Stunted or Stressed Plants (D1) _ Iron Deposits (135) X Geomorphic Position (D2) _ Inundation Visible on Aerial Imagery (137) _Shallow Aquitard (D3) —Water-Stained Leaves (139) _ Microtopographic Relief (D4) Aquatic Fauna (1313) FAC-Neutral Test (D5) Field Observations: Surface Water Present? Yes_ No X Depth (inches): Water Table Present? Yes_ No X Depth (inches): Saturation Present? Yes_ No X Depth (inches): Wetland Hydrology Present? Yes X No (includes capillary fringe) Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: Remarks: ENG FORM 6116-4, JUL 2018 Eastern Mountains and Piedmont —Version 2.0 Delineation of Wetlands and Waters— Mouth of Hardin Creek Restoration Project 10 Jennings Environmental PLLC VEGETATION (Four Strata) - Use scientific names of plants. Sampling Point: Upland Absolute Dominant Indicator Tree Stratum (Plot size: ) % Cover Species? Status Dominance Test worksheet: 1. Number of Dominant Species 2. That Are OBL, FACW, or FAC: 1 (A) 3. Total Number of Dominant 4. Species Across All Strata: 4 (B) 5. Percent of Dominant Species 6. That Are OBL, FACW, or FAC: 25.0 % (A/B) 7. Prevalence Index worksheet: =Total Cover Total % Cover of: Multiply by: 50 % of total cover: 20 % of total cover: OBL species 0 x 1 = 0 Sapling/Shrub Stratum (Plot size: ) FACW species 42 x 2 = 84 1. FAC species 2 x 3 = 6 2. FACU species 33 x 4 = 132 3. UPL species 2 x 5 = 10 4. Column Totals: 79 (A) 232 (B) 5. Prevalence Index = B/A = 2.94 6. Hydrophytic Vegetation Indicators: 7. _ 1 - Rapid Test for Hydrophytic Vegetation 8. -2 - Dominance Test is >50 9. X 3 - Prevalence Index is !-3.0' =Total Cover 4 - Morphological Adaptations' (Provide supporting 50 % of total cover: 20 % of total cover: data in Remarks or on a separate sheet) Herb Stratum (Plot size: 5-ft ) -Problematic Hydrophytic Vegetation' (Explain) 1. phalaris arundinacea 40 Yes FACW 11ndicators of hydric soil and wetland hydrology must be 2. solidago canadensis 25 Yes FACU present, unless disturbed or problematic. Definitions of Four Vegetation Strata: 3. persicaria perfoliata 1 No FAC 4. juncus effusus 1 No FACW Tree -Woody plants, excluding vines, 3 in. (7.6 cm) or 5. achillea millefolium 1 No FACU more in diameter at breast height (DBH), regardless of 6. symphyotrichum oblongifolium 2 No UPL height. 7. eupatorium fistulosum 1 No FACW Sapling/Shrub - Woody plants, excluding vines, less 8. carpinus caroliniana 1 No FAC than 3 in. DBH and greater than or equal to 3.28 ft 9 (1 m) tall. 10. Herb -All herbaceous (non -woody) plants, regardless 11. of size, and woody plants less than 3.28 ft tall. 72 =Total Cover Woody Vine - All woody vines greater than 3.28 ft in 50 % of total cover: 36 20 % of total cover: 15 height. Woody Vine Stratum (Plot size: 30-ft ) 1. rubus allagheniensis 5 Yes FACU 2. rosa multiflora 2 Yes FACU 3. 4. 5. Hydrophytic 7 =Total Cover Vegetation 50 % of total cover: 4 20 % of total cover: 2 Present? Yes X No Remarks: (Include photo numbers here or on a separate sheet.) ENG FORM 6116-4, JUL 2018 Eastern Mountains and Piedmont - Version 2.0 Delineation of Wetlands and Waters- Mouth of Hardin Creek Restoration Project 11 Jennings Environmental PLLC SOIL Sampling Point: Upland Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % Type' Loc2 Texture Remarks 0-8 10YR 4/3 100 Loamy/Clayey Silty clay loam with sand 8-15 10YR 4/4 100 Loamy/Clayey Silty clay loam with sand 'Type: C=Concentration, D=Depletion, RM=Reduced Matrix, MS=Masked Sand Grains. 2Location: PL=Pore Lining, M=Matrix. Hydric Soil Indicators: Indicators for Problematic Hydric Soils': _ Histosol (Al) _ Polyvalue Below Surface (S8) (MLRA 147, 148) _2 cm Muck (A10) (MLRA 147) _ Histic Epipedon (A2) _Thin Dark Surface (S9) (MLRA 147, 148) _Coast Prairie Redox (A16) —Black Histic (A3) —Loamy Mucky Mineral (F1) (MLRA 136) (MLRA 147, 148) _ Hydrogen Sulfide (A4) _ Loamy Gleyed Matrix (F2) _ Piedmont Floodplain Soils (F19) —Stratified Layers (A5) _ Depleted Matrix (F3) (MLRA 136, 147) _ 2 cm Muck (A10) (LRR N) _ Redox Dark Surface (F6) —Red Parent Material (F21) _ Depleted Below Dark Surface (A11) —Depleted Dark Surface (F7) (outside MLRA 127, 147, 148) _ Thick Dark Surface (Al2) _ Redox Depressions (F8) —Very Shallow Dark Surface (F22) _Sandy Mucky Mineral (S1) _ Iron -Manganese Masses (F12) (LRR N, _Other (Explain in Remarks) _Sandy Gleyed Matrix (S4) MLRA 136) _Sandy Redox (S5) _ Umbric Surface (F13) (MLRA 122, 136) 'Indicators of hydrophytic vegetation and _Stripped Matrix (S6) _Piedmont Floodplain Soils (F19) (MLRA 148) wetland hydrology must be present, Dark Surface (S7) Red Parent Material (F21) (MLRA 127, 147, 148) unless disturbed or problematic. Restrictive Layer (if observed): Type: Depth (inches): Hydric Soil Present? Yes No X Remarks: ENG FORM 6116-4, JUL 2018 Eastern Mountains and Piedmont — Version 2.0 Delineation of Wetlands and Waters— Mouth of Hardin Creek Restoration Project 12 Jennings Environmental PLLC U.S. Army Corps of Engineers OMB Control #: 0710-0024, Exp:1113012024 WETLAND DETERMINATION DATA SHEET — Eastern Mountains and Piedmont Region Requirement Control Symbol EXEMPT., See ERDC/EL TR-12-9; the proponent agency is CECW-CO-R (Authority: AR 335-15, paragraph 5-2a) Project/Site: Mouth of Hardin Creek Restoration Applicant/Owner: Jennings Environmental, PLLC City/County: Boone, Watauga County Sampling Date: 9/14-15/23 State: NC Sampling Point: W3 Investigator(s): D. Brown Section, Township, Range: N/A Landform (hillside, terrace, etc.): Floodplain bench Local relief (concave, convex, none): None Slope (%): 1-3% Subregion (LRR or MLRA): LRR N Lat: 36.21257 Long:-81.64999 Datum: NAD 1983 Soil Map Unit Name: Rosman (RoA) and Nikwasi (NkA) NWI classification: N/A Are climatic / hydrologic conditions on the site typical for this time of year? Yes X No (If no, explain in Remarks.) Are Vegetation X , Soil X , or Hydrology X significantly disturbed? Are "Normal Circumstances" present? Yes X No Are Vegetation , Soil , or Hydrology naturally problematic? (If needed, explain any answers in Remarks.) SUMMARY OF FINDINGS — Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes X No I Is the Sampled Area Hydric Soil Present? Yes X No within a Wetland? Yes X No Wetland Hydrology Present? Yes X No Remarks: Pre-1990's the site was in agricutural use (pasture & crops). During the last 30-35 years the site has naturlized. Sewerline construction & greenway development have disturbed the hydrology, soils & vegetation. Reed canary grass (phalaris arundinacea) is a dominant herbaceous species in open areas. HYDROLOGY Wetland Hydrology Indicators: Secondary Indicators (minimum of two required) Primary Indicators (minimum of one is required: check all that apply) _Surface Soil Cracks (136) _Surface Water (Al) _True Aquatic Plants (1314) _Sparsely Vegetated Concave Surface (138) _High Water Table (A2) _Hydrogen Sulfide Odor (Cl) _Drainage Patterns (1310) _Saturation (A3) X Oxidized Rhizospheres on Living Roots (C3) _Moss Trim Lines (1316) _Water Marks (131) _Presence of Reduced Iron (C4) _Dry -Season Water Table (C2) X Sediment Deposits (132) _Recent Iron Reduction in Tilled Soils (C6) X Crayfish Burrows (C8) _Drift Deposits (133) _Thin Muck Surface (C7) _Saturation Visible on Aerial Imagery (C9) _Algal Mat or Crust (134) _Other (Explain in Remarks) _Stunted or Stressed Plants (D1) _Iron Deposits (135) X Geomorphic Position (D2) _Inundation Visible on Aerial Imagery (137) _ShallowAquitard (D3) X Water -Stained Leaves (139) X Microtopographic Relief (D4) Aquatic Fauna (1313) X FAC-Neutral Test (D5) Field Observations: Surface Water Present? Yes_ No X Depth (inches): Water Table Present? Yes_ No X Depth (inches): Saturation Present? Yes_ No X Depth (inches): Wetland Hydrology Present? Yes X No (includes capillary fringe) Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: Remarks: ENG FORM 6116-4, JUL 2018 Eastern Mountains and Piedmont — Version 2.0 Delineation of Wetlands and Waters— Mouth of Hardin Creek Restoration Project 13 Jennings Environmental PLLC VEGETATION (Four Strata) - Use scientific names of plants. Sampling Point: W3 Absolute Dominant Indicator Tree Stratum (Plot size: ) % Cover Species? Status Dominance Test worksheet: 1. Number of Dominant Species 2. That Are OBL, FACW, or FAC: 2 (A) 3. Total Number of Dominant 4. Species Across All Strata: 2 (B) 5. Percent of Dominant Species 6. That Are OBL, FACW, or FAC: 100.0 % (A/B) 7. Prevalence Index worksheet: =Total Cover Total % Cover of: Multiply by: 50 % of total cover: 20 % of total cover: OBL species 20 x 1 = 20 Sapling/Shrub Stratum (Plot size: ) FACW species 87 x 2 = 174 1. FAC species 5 x 3 = 15 2. FACU species 0 x 4 = 0 3. UPL species 0 x 5 = 0 4. Column Totals: 112 (A) 209 (B) 5. Prevalence Index = B/A = 1.87 6. Hydrophytic Vegetation Indicators: 7. _ 1 - Rapid Test for Hydrophytic Vegetation 8. X 2 - Dominance Test is >50 9. X 3 - Prevalence Index is !2.0' =Total Cover 4 - Morphological Adaptations' (Provide supporting 50 % of total cover: 20 % of total cover: data in Remarks or on a separate sheet) Herb Stratum (Plot size: 5-ft ) -Problematic Hydrophytic Vegetation' (Explain) 1. phalaris arundinacea 50 Yes FACW 'Indicators of hydric soil and wetland hydrology must be 2. mentha arvensis 30 Yes FACW present, unless disturbed or problematic. Definitions of Four Vegetation Strata: 3. impatiens capensis 5 No FACW 4. leersia oryzoides 20 No OBL Tree - Woody plants, excluding vines, 3 in. (7.6 cm) or 5. persicaria perfoliata 5 No FAC more in diameter at breast height (DBH), regardless of 6. juncus effusus 1 No FACW height. 7. scirpus cyperinus 1 No FACW Sapling/Shrub- Woody plants, excluding vines, less 8. than 3 in. DBH and greater than or equal to 3.28 ft 9 (1 m) tall. 10. Herb -All herbaceous (non -woody) plants, regardless 11. of size, and woody plants less than 3.28 ft tall. 112 =Total Cover Woody Vine - All woody vines greater than 3.28 ft in 50% of total cover: 56 20% of total cover: 23 height. Woody Vine Stratum (Plot size: ) 1. 2. 3. 4. 5. Hydrophytic =Total Cover Vegetation 50 % of total cover: 20 % of total cover: Present? Yes X No Remarks: (Include photo numbers here or on a separate sheet.) ENG FORM 6116-4, JUL 2018 Eastern Mountains and Piedmont -Version 2.0 Delineation of Wetlands and Waters- Mouth of Hardin Creek Restoration Project 14 Jennings Environmental PLLC SOIL Sampling Point: W3 Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features (inches) Color (moist) % Color (moist) % Type' Loc' Texture Remarks 0-4 10YR 2/1 100 Loamy/Clayey Silty clay loam with sand 4-15 10YR 3/1 90 7.5YR 4/2 10 D M Loamy/Clayey Silty clay loam with sand Hydric Soil Indicators: _Histosol (Al) Histic Epipedon (A2) —Black Histic (A3) —Hydrogen Sulfide (A4) _Stratified Layers (A5) 2 cm Muck (A10) (LRR N) _ Depleted Below Dark Surface (A11) _Thick Dark Surface (Al 2) _Sandy Mucky Mineral (S1) _Sandy Gleyed Matrix (S4) _Sandy Redox (S5) _Stripped Matrix (S6) Dark Surface (S7) Restrictive Layer (if observed): Type: Depth (inches): Remarks: ENG FORM 6116-4, JUL 2018 RM=Reduced Matrix, MS=Masked Sand Grains. _ Polyvalue Below Surface (S8) (MLRA 147, 148) _Thin Dark Surface (S9) (MLRA 147, 148) _Loamy Mucky Mineral (F1) (MLRA 136) —Loamy Gleyed Matrix (F2) X Depleted Matrix (F3) _ Redox Dark Surface (F6) —Depleted Dark Surface (F7) _ Redox Depressions (F8) _ Iron -Manganese Masses (F12) (LRR N, MLRA 136) _ Umbric Surface (F13) (MLRA 122, 136) _ Piedmont Floodplain Soils (F19) (MLRA 148) Red Parent Material (F21) (MLRA 127, 147, 148) 2Location: PL=Pore Lining, M=Matrix Indicators for Problematic Hydric Soil: 2 cm Muck (A10) (MLRA 147) _Coast Prairie Redox (A16) (MLRA 147, 148) —Piedmont Floodplain Soils (F19) (MLRA 136, 147) _Red Parent Material (F21) (outside MLRA 127, 147, 148) _Very Shallow Dark Surface (F22) Other (Explain in Remarks) 3Indicators of hydrophytic vegetation and wetland hydrology must be present, unless disturbed or problematic. Hydric Soil Present? Yes X No Eastern Mountains and Piedmont —Version 2.0 Delineation of Wetlands and Waters— Mouth of Hardin Creek Restoration Project 15 Jennings Environmental PLLC APPENDIX C. 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