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HomeMy WebLinkAbout20200511 Ver 1_EB-6038_PJD Package_20200312_20200414Preliminary ORM Data Entry Fields for New Actions ACTION ID #: SAW- 2020-00346 Prepare file folder ❑✓ 1. Project Name [PCN Form A2a]: EB-6038 Begin Date (Date Received): Assign Action ID Number in ORM ❑✓ 2. Work Type: ❑Private ❑Institutional ❑✓ Government ❑ Commercial 3. Project Description / Purpose [PCN Form B3d and B3e]: New Multi -use path and adjacent roadway improvements 4. Property Owner / Applicant [PCN Form A3 or A4]: City of Hickory 5. Agent / Consultant [PNC Form A5 — or ORM Consultant ID Number]: TGS Engineers 6. Related Action ID Number(s) [PCN Form B5b]: 7. Project Location— Coordinates, Street Address, and/or Location Description [PCN Form Blb]: Latitude: 35.744891 ON, Longitude: 81.372268°W, Multi -use trail from US 321 to Hickory Regional Airport, and from 9th St. NW to 11th St. NW 8. Project Location— Tax Parcel ID [PCN Form Bla]: Multiple 9. Project Location — County [PCN Form A2b]: Catawba and Burke 10. Project Location — Nearest Municipality or Town [PCN Form A2c]: Hickory 11. Project Information — Nearest Waterbody [PCN Form 132a]: Catawba River 12. Watershed / 8-Digit Hydrologic Unit Code [PCN Form 132c]: 03050101 Authorization: Section 10 ❑ Section 404 ❑✓ Regulatory Action Type: ❑ Standard Permit Nationwide Permit # Regional General Permit # Jurisdictional Determination Request Section 10 and 404 ❑ ❑ Pre -Application Request ❑ Unauthorized Activity ❑ Compliance ❑ No Permit Required Revised 20150602 TGS ENGINEERS ried o� m 00 c� o� X Q Cb Cb 00 m rn rn v Z Z O fi U) m rn coo oc�u o U n z c p —0-C = C)J CD W O N ry C0 L m c w U) March 12, 2020 Ms. Catherine M. Janiczak Regulatory Specialist U.S. Army Corps of Engineers Charlotte Regulatory Satellite Office c/o 151 Patton Avenue, Room 208 Asheville, NC 28801-5006 Catherine.M.Janiczak@usace.army.mil SUBJECT: Action ID Number SAW-2020-00346 STIP Project Number EB-6038 Multi -Use Trail from US 321 to Hickory Regional Airport, and from 9t" Street NW to 11t" Street NW Catawba and Burke Counties Dear Ms. Janiczak, Enclosed is a Preliminary Jurisdictional Determination (PJD) package for your review, which includes the following attachments: ■ Figure 1— Vicinity Map ■ Figure 2 — USGS Topographic Map ■ Figure 3 — Potential Jurisdictional Features Map ■ USACE Wetland Determination Data Forms ■ USACE Upland Data Forms ■ Waters Upload Spreadsheet (ORM) ■ NCWAM Forms (all wetlands) ■ NCDWQ Stream Identification Forms ■ Preliminary JD Form ■ Jurisdictional Determination Request Form ■ Property Owner Info Landowner property access notification letters have been mailed and include reference to the USACE site visit. The GPS equipment utilized to locate features on this project was a Trimble Geo 7 Series sub - meter accurate GPS receiver. The following tables provides a summary of stream and wetland characteristics for features within the project study area. Table 1. Streams in the studv area Stream Name Map ID NCDWR Index Number Best Usage Classification UT to Catawba River SA 11-(51) WS-IV, B; CA UT to Catawba River SB 11-(51) WS-IV, B; CA UT to Catawba River Sc 11-(51) WS-IV, B; CA Frye Creek SD 11-54-1 WS-IV TGS ENGINEERS di o� m 00 c� r\ r` rn m Q 00 00 00 m rn W 0 a +; U) m -C o rn m 0 c0u o U -o z �o —0-C =CU•m co W Q) o U)a Q) Q) c 'm c w U) c.� Table 2. Phvsical characteristics of streams in the studv area Bank Bankful Water Map Height Width Depth Channel Substrate Velocity Clarity ID (ft) (ft) (in) SA 0.5-3 1-5 2-18 Silt, sand, gravel, cobble Moderate Clear SB 0-1 1-3 1-4 Sand, gravel Slow Clear SC 0-1 1-3 1-3 Sand, gravel, cobble Moderate Clear Slightly SD 1-2 1-3 3-6 Sand, gravel, cobble Moderate turbid Table 3. Jurisdictional characteristics of streams in the studv area Map Length Compensatory Figure ID (ft) Classification Mitigation River Basin Buffer Number Required No (<150' of No (Not mapped on SA 918 Perennial anticipated USGS or Soils maps) 3-1 impacts) SB 21 Ephemeral No (No impacts No (Not mapped on 3 2 anticipated) USGS or Soils maps) No (No impacts No (Not mapped on SC 60 Intermittent anticipated) USGS or Soils maps) 3 2 No (Bank SD 174 Intermittent stabilization) Yes 3-4 TOTAL 1173 Table 4. Jurisdictional characteristics of wetlands in the study area MAP NCWAM NCWAM Hydrologic Figure Area (ac) ID Classification Rating Classification Number WA Basin Wetland Medium Non -riparian 0.82 3-2 WC Basin Wetland Medium Non -riparian 0.16 3-2 WD Headwater Forest High Riparian 0.01 3-1 WE Headwater Forest High Riparian 0.03 3-1 Non -tidal WF Medium Riparian 0.09 3-1 Freshwater Marsh TOTAL 1 1.11 Please contact me at 919.773.8887 ext. 125 or via email at ryan.elliott@tgsengineers.com or David Petty, PE, who will be preparing and submitting the permit application, at 919.773.8887 ext. 104 or via email at dpetty@tgsengineers.com if you have any questions or would like additional information. Sincerely, Ryan Elliott Environmental Scientist cc: Kevin B. Greer, PE, DS-A, CS-4, City Engineer, City of Hickory David B. Petty, PE, TGS Engineers Legend Project Study Area —+— Railroads / 1 County Boundary City Boundary vl el % f --� 1 I � I / I jJ 1 i ---F tiv Hickory Regiorml ll Arport I / I / I% 1) J 2rrd Ave NW 0r=--�' Long View j 0 0.25 0.5 1 iii Miles C4 `- Park 11 y / - I �? Z k- �I,LI._, � Ii Caldwell CO. Catawba CO� ta1E Hk Iknry rC e Tenn Hiplon �fh Town club Civic Park �r 17,, Srf� YR STI P Hickor EB-6038 �S Z52 La 3rd' Ave NW 3 2nd Ave Nil1(= - HI 1 s t A'.'e NA, 2ndAve SW tst Ave sW cn cn N y { rn 7) t Ave SW u� N V aU Us.xa sbY v, r, ESRI World Street Basemab CALDWELL BtMiKLEbri ALEXANDER IREDELL S rooktorcl CATAWBA LINC66 -------- N.T.S. TGS VICINITY MAP E M qE ERS STIP PROJECT #EB-6038 FIGURE MULTI -USE TRAIL FROM US 321 TO HICKORY rddp REGIONAL AIRPORT, AND FROM 9TH ST NW TO 11TH ST NW Date: 3-12-2020 BURKE AND CATAWBA COUNTIES Legend Project Study Area a i d I� t t— 24K Quadrangle Index . 1 iLOtRY �v Gmaite-Falls-Befhlehem I WELL STIP 06 EB-6038 r� ^ uli'nt -al i E am ?dkS� ray- '�` - ��•�' - ( ^., `'1� _ � :. II ,-R _ x Loniview i; IMF ��• . ^dam - ��f • - �8T Lorlgvi 'I step E` I j Air.,' r 7 POO -i. ��♦- > WRF' SAY iY Id t 0 1,000 2,000 4,000 Gjt Source: USA Topo Maps Web Map Service Feet (USGS Quadrangles: Granite Falls, Bethlehem, Longview, & Hickory) TGS USGS TOPOGRAPHIC MAP EMs EERS STIP PROJECT#EB-6038 FIGURE MULTI -USE TRAIL FROM US 321 TO HICKORY rdgpd REGIONAL AIRPORT, AND FROM 9TH ST NW TO 11TH ST NW Date: 3-12-2020 BURKE AND CATAWBA COUNTIES b 4*-. - r WL rl I I I II I � I II .. WE WET W� WE UP WD WET AV D \,\ �j RN it 1 i W SR-1625 Figure 3-1 Potential Jurisdiction Features EB-6038 Burke and Catawba Counties -4 Date: 3-12-2020 1 inch = 200 feet 0 100 200 Legend o Data Points Potential Wetland WoUS Railroads 400 Project Study Area Perennial Stream — — Municipal Boundary Feet L- � Sheet Border Intermittent Stream -_ _ County Boundary Imagery Source: NC OneMap 2018 Orthoimagery meral Stream I r rr 1 r, I I 1 1 I I 1 1 I 1 I 1 1 _ _ � EGG r,r � •+ E �t ,ir,�� i�. .. -: SC WA Jf - _---- — Y F�. Figure 3-2 Potential Jurisdiction Features EB-6038 Burke and Catawba Counties Hickory- y r -� __, 1 � � f Legend N 1 inch = 200 feet o Data Points 0 100 200 400 Project Study Area Feet Sheet Border Date: 3-12-2020 Imagery Source: NC OneMap 2018 Orthoimagery ,A Potential Wetland WoUS Railroads Perennial Stream — — Municipal Boundary Intermittent Stream — — County Boundary Ephemeral Stream !_ - ,v J - 3 - Vb OF or - __ .. �;• - -' % �r, - �'� • - ' - 'ram :. v i .V- + ,r W ! r• , A^ �' 1iY OLD LENOIR RD r - .1 STOR STp� Nw. N /�/(� f ti r• r RXlk a.' .. 21 321 HWY 321 NI/� ` t • r, p 1 :r • . ♦� � �_` ����� - - my `��/ `� r - � � I n- • -F � � �t .ate, �' •.ic f ?� Q w Legend Figure 3-3 1 inch = 200 feet o Data Points Potential Wetland WoUS Railroads Potential Jurisdiction Features---- 0 100 200 400 � Project Study Area Perennial Stream Municipal Boundary EB-6038 Feet r Sheet Border Intermittent Stream County Boundary Burke and Catawba Counties Date: 3-12-2020 Imagery Source: NC OneMap 2018 Orthoimagery Ephemeral Stream THST PL NW �• O1?- 10 T 10TH-S7BVVD'NW ti Z QL _ O 11THSTNWdo ix y � - - 127- H ST NW ST pR �•1W `� r Z„F� z tot. J �. � � P ♦� '� C1s'�* - -_ @ ice. ' - � � � �. � Legend Figure 3-4 1 inch = 200 feet o Data Points Potential Wetland WoUS Railroads Potential Jurisdiction Features-----1 Z � 0 100 200 aoo � Project Study Area Perennial Stream Municipal Boundary EB-6038 Feet r Sheet Border Intermittent Stream County Boundary Burke and Catawba Counties Date: 3-12-2020 Imagery Source: NC OneMap 2018 Orthoimagery Ephemeral Stream .r z t: i W ,► MAIN AV DR, NW - . ' _ 1 Figure 3-5 Potential Jurisdiction Features EB-6038 Burke and Catawba Counties `�; k v •,: MAIN AV NW 1 � 1 1 Si , + Hickor ` z F 1STAV NW C/)_ —OLIIV am — A. I Y at i t � l MAIN AV SW w N EMT- j- ion OEM" I � ��_ SR-1692 1ST AV SW W"_ - 41- U) 7-7 ! SR-2231 2ND AV SW i -r Jar �.y - +l�' Y! • ' M 1 Legend N 1 inch = 200 feet o Data Points 0 100 200 400 Project Study Area Feet Sheet Border Date: 3-12-2020 Imagery Source: NC OneMap 2018 Orthoimagery q w � Wk co ilk�'- CO �co t>� _ r Potential Wetland WoUS Railroads Perennial Stream — — Municipal Boundary Intermittent Stream — — County Boundary Ephemeral Stream WETLAND DETERMINATION DATA SHEET — Eastern Mountains and Piedmont Region Project/Site: EB-6038 City/County: Hickory, Catawba Sampling Date: 1/14/20 Applicant/Owner: City of Hickory, Outbox Hickory LLC State: NC Sampling Point: WA UPL Investigator(s): Ryan Elliott Section, Township, Range: Hickory Landform (hillside, terrace, etc.): Hillslope Local relief (concave, convex, none): Convex Slope (%): 4 Subregion (LRR or MLRA): LRR P, MLRA 136 Lat: 35.748944 Long:-81.373217 Datum: WGS84 Soil Map Unit Name: FcC: Fairview gravelly fine sandy loam NWI classification: None Are climatic / hydrologic conditions on the site typical for this time of year? Yes X No (If no, explain in Remarks.) Are Vegetation Soil or Hydrology 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: 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 (A1) _True Aquatic Plants (1314) _Sparsely Vegetated Concave Surface (138) X High Water Table (A2) _ Hydrogen Sulfide Odor (Cl) —Drainage Patterns (1310) X Saturation (A3) -Oxidized Rhizospheres on Living Roots (C3) _ Moss Trim Lines (B16) —Water Marks (61) _ Presence of Reduced Iron (C4) _ Dry -Season Water Table (C2) —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) _ Geomorphic Position (D2) _ Inundation Visible on Aerial Imagery (137) —Shallow Aquitard (D3) —Water-Stained Leaves (69) _ Microtopographic Relief (D4) Aquatic Fauna (1313) FAC-Neutral Test (D5) Field Observations: Surface Water Present? Yes No X Depth (inches): Water Table Present? Yes X No Depth (inches): 4 Saturation Present? Yes X No Depth (inches): 0 Wetland Hydrology Present? Yes X No (includes capillary fringe) Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: Remarks: High water table and saturation were likely due to rain events prior to and during delineation. US Army Corps of Engineers Eastern Mountains and Piedmont — Version 2.0 VEGETATION (Four Strata) - Use scientific names of plants. Sampling Point: WA UPL Tree Stratum (Plot size: 30' ) 1. Pinus taeda 2. 3. 4. 5. 6. 7. 50% of total cover: 15 Sapling/Shrub Stratum (Plot size: 15' ) 1. Pinus taeda 2. 3. 4. 5. 6. 7. 8. 9. 50% of total cover: 3 Herb Stratum (Plot size: 5' ) 1. 2. 3. 4. 5. 6. 7. 8. 9. 10. 11. 50% of total cover: Woody Vine Stratum (Plot size: 15' ) 1. Lonicera japonica 2. Toxicodendron radicans 3. 4. 5. Absolute Dominant Indicatc % Cover Species? Status 30 Yes FAC 30 =Total Cover 20% of total cover: 6 5 Yes FAC 20% of total cover: 1 20% of total cover: 10 Yes FACU 5 Yes FAC 15 =Total Cover 50% of total cover: 8 20% of total cover: 3 Remarks: (Include photo numbers here or on a separate sheet.) Dominance Test worksheet: Number of Dominant Species That Are OBL, FACW, or FAC: 3 (A) Total Number of Dominant Species Across All Strata: 4 (B) Percent of Dominant Species That Are OBL, FACW, or FAC: 75.0% (A/B) Prevalence Index worksheet: Total % Cover of: Multiply by: OBL species 0 x 1 = 0 FACW species 0 x 2 = 0 FAC species 40 x 3 = 120 FACU species 10 x 4 = 40 UPL species 0 x 5 = 0 Column Totals: 50 (A) 160 (B) Prevalence Index = B/A = 3.20 Hydrophytic Vegetation Indicators: _ 1 - Rapid Test for Hydrophytic Vegetation X 2 - Dominance Test is >50% -3 Prevalence Index is :53.0' 4 - Morphological Adaptations' (Provide supporting data in Remarks or on a separate sheet) Problematic Hydrophytic Vegetation' (Explain) 'Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Definitions of Four Vegetation Strata: Tree - Woody plants, excluding vines, 3 in. (7.6 cm) or more in diameter at breast height (DBH), regardless of height. Sapling/Shrub - Woody plants, excluding vines, less than 3 in. DBH and greater than or equal to 3.28 ft (1 m) tall. Herb - All herbaceous (non -woody) plants, regardless of size, and woody plants less than 3.28 ft tall. Woody Vine - All woody vines greater than 3.28 ft in height. Hydrophytic Vegetation Present? Yes X No US Army Corps of Engineers Eastern Mountains and Piedmont - Version 2.0 SOIL Sampling Point: WA UPL 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) % Types Loc2 Texture Remarks 0-2 10YR 2/2 100 Loamy/Clayey 2-8 10YR 3/4 100 Loamy/Clayey 'Type: C=Concentration, D=Depletion, RM=Reduced Matrix, MS=Masked Sand Grains. 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: Weathered Rock Depth (inches): 8 _ Polyvalue Below Surface (S8) (MLRA 147, 148) _Thin Dark Surface (S9) (MLRA 147, 148) —Loamy Mucky Mineral (F1) (MLRA 136) _ Loamy Gleyed Matrix (F2) _ 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 Soils3: 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 No X Remarks: This data sheet is revised from Eastern Mountains and Piedmont Regional Supplement Version 2.0 to include the NRCS Field Indicators of Hydric Soils, Version 8.0, 2016. The restictive layer appeared to be weathered rock and was difficult to impossible to get an auger through. US Army Corps of Engineers Eastern Mountains and Piedmont — Version 2.0 WETLAND DETERMINATION DATA SHEET — Eastern Mountains and Piedmont Region Project/Site: EB-6038 City/County: Hickory, Catawba Sampling Date: 1/14/20 Applicant/Owner: City of Hickory, Outbox Hickory LLC State: NC Sampling Point: WA WET Investigator(s): Ryan Elliott Section, Township, Range: Hickory Landform (hillside, terrace, etc.): Basin Local relief (concave, convex, none): Concave Slope (%): 1 Subregion (LRR or MLRA): LRR P, MLRA 136 Lat: 35.748926 Long:-81.373102 Datum: WGS84 Soil Map Unit Name: FaE3: Fairview clay loam NWI classification: None Are climatic / hydrologic conditions on the site typical for this time of year? Yes X No (If no, explain in Remarks.) Are Vegetation Soil X or Hydrology significantly disturbed? Are "Normal Circumstances" present? Yes No X Are Vegetation X 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 X No within a Wetland? Yes X No Wetland Hydrology Present? Yes X No Remarks: Invasive Pyrus calleryana seems to have spread into the area considerably since 2018 aerial photos. 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) X Surface Water (A1) _True Aquatic Plants (1314) _Sparsely Vegetated Concave Surface (138) X High Water Table (A2) _ Hydrogen Sulfide Odor (Cl) X Drainage Patterns (610) X Saturation (A3) -Oxidized Rhizospheres on Living Roots (C3) _ Moss Trim Lines (B16) —Water Marks (61) _ Presence of Reduced Iron (C4) _ Dry -Season Water Table (C2) —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) _ Geomorphic Position (D2) _ Inundation Visible on Aerial Imagery (137) —Shallow Aquitard (D3) X Water -Stained Leaves (69) _ Microtopographic Relief (D4) X Aquatic Fauna (1313) X FAC-Neutral Test (D5) Field Observations: Surface Water Present? Yes X No Depth (inches): 4 Water Table Present? Yes X No Depth (inches): 0 Saturation Present? Yes X No Depth (inches): 0 Wetland Hydrology Present? Yes X No (includes capillary fringe) Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: Remarks: Various frogs, including Pseudacris crucifer, were heard calling throughout the wetland area during the field visit. US Army Corps of Engineers Eastern Mountains and Piedmont — Version 2.0 VEGETATION (Four Strata) - Use scientific names of plants. Sampling Point: WA WET Absolute Dominant Indicato Tree Stratum (Plot size: 30' ) % Cover Species? Status 1. 2. 3. 4. 5. 6. 7. =Total Cover 50% of total cover: 20% of total cover: Sapling/Shrub Stratum (Plot size: 15' ) 1. Salix nigra 30 Yes OBL 2. Acer negundo 5 No FAC 3. Pinus taeda 2 No FAC 4. 5. 6. 7. 8. 9. 37 =Total Cover 50% of total cover: 19 20% of total cover: 8 Herb Stratum (Plot size: 5' ) 1. Juncus effusus 15 Yes FACW 2. Cyperus odoratus 10 Yes FACW 3. Scirpus cyperinus 5 No FACW 4. Rosa multiflora 5 No FACU 5. 6. 7. 8. 9. 10. 11. 35 =Total Cover 50% of total cover: 18 20% of total cover: 7 Woody Vine Stratum (Plot size: 15' ) 1. 2. 3. 4. 5. Dominance Test worksheet: Number of Dominant Species That Are OBL, FACW, or FAC: 3 (A) Total Number of Dominant Species Across All Strata: 3 (B) Percent of Dominant Species That Are OBL, FACW, or FAC: 100.0% (A/B) Prevalence Index worksheet: Total % Cover of: Multiply by: OBL species 30 x 1 = 30 FACW species 30 x 2 = 60 FAC species 7 x 3 = 21 FACU species 5 x 4 = 20 UPL species 0 x 5 = 0 Column Totals: 72 (A) 131 (B) Prevalence Index = B/A = 1.82 _ 1 - Rapid Test for Hydrophytic Vegetation X 2 - Dominance Test is >50% X 3 - Prevalence Index is :53.0' 4 - Morphological Adaptations' (Provide supporting data in Remarks or on a separate sheet) Problematic Hydrophytic Vegetation' (Explain) 'Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Definitions of Four Vegetation Strata: Tree - Woody plants, excluding vines, 3 in. (7.6 cm) or more in diameter at breast height (DBH), regardless of height. Sapling/Shrub - Woody plants, excluding vines, less than 3 in. DBH and greater than or equal to 3.28 ft (1 m) tall. Herb - All herbaceous (non -woody) plants, regardless of size, and woody plants less than 3.28 ft tall. Woody Vine - All woody vines greater than 3.28 ft in height. Hydrophytic =Total Cover Vegetation 50% of total cover: 20% of total cover: I Present? Yes X No Remarks: (Include photo numbers here or on a separate sheet.) A patch of invasive Pyrus calleryana seems to have spread significantly into the wetland as compared to aerial imagery from March of 2018 US Army Corps of Engineers Eastern Mountains and Piedmont - Version 2.0 SOIL Sampling Point: WA WET 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) % Types Loc2 Texture Remarks 0-3 10YR 4/2 100 3-6 10YR 4/2 85 7.5YR 5/8 15 C M Loamy/Clayey Prominent redox concentrations '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 Soils3: _ 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) X 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) X 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) 3Indicators 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: Weathered rock Depth (inches): 6 Hydric Soil Present? Yes X No Remarks: This data sheet is revised from Eastern Mountains and Piedmont Regional Supplement Version 2.0 to include the NRCS Field Indicators of Hydric Soils, Version 8.0, 2016. The restrictive layer appeared to be weathered rock and was difficult to impossible to get an auger through. Soils were inconsistent and varied considerably. US Army Corps of Engineers Eastern Mountains and Piedmont — Version 2.0 WETLAND DETERMINATION DATA SHEET — Eastern Mountains and Piedmont Region Project/Site: EB-6038 City/County: Hickory, Catawba Sampling Date: 1/27/20 Applicant/Owner: City of Hickory, Jag Properties LLC State: NC Sampling Point: WC UPL Investigator(s): Ryan Elliott Section, Township, Range: Hickory Landform (hillside, terrace, etc.): Hillslope Local relief (concave, convex, none): Convex Slope (%): 3 Subregion (LRR or MLRA): LRR P, MLRA 136 Lat: 35.748849 Long:-81.371467 Datum: WGS84 Soil Map Unit Name: FcC: Fairview gravelly fine sandy loam NWI classification: None Are climatic / hydrologic conditions on the site typical for this time of year? Yes X No (If no, explain in Remarks.) Are Vegetation Soil or Hydrology 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 No X Is the Sampled Area Hydric Soil Present? Yes No X within a Wetland? Yes No X Wetland Hydrology Present? Yes X No Remarks: 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 (A1) _True Aquatic Plants (1314) _Sparsely Vegetated Concave Surface (138) X High Water Table (A2) _ Hydrogen Sulfide Odor (Cl) —Drainage Patterns (1310) X Saturation (A3) -Oxidized Rhizospheres on Living Roots (C3) _ Moss Trim Lines (B16) —Water Marks (61) _ Presence of Reduced Iron (C4) _ Dry -Season Water Table (C2) —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) _ Geomorphic Position (D2) _ Inundation Visible on Aerial Imagery (137) —Shallow Aquitard (D3) —Water-Stained Leaves (69) _ Microtopographic Relief (D4) Aquatic Fauna (613) FAC-Neutral Test (D5) Field Observations: Surface Water Present? Yes No X Depth (inches): Water Table Present? Yes X No Depth (inches): 4 Saturation Present? Yes X No Depth (inches): 0 Wetland Hydrology Present? Yes X No includes capillary fringe Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: Remarks: Presence of hydrology is likely due to rainfall events prior to the visit. US Army Corps of Engineers Eastern Mountains and Piedmont — Version 2.0 VEGETATION (Four Strata) - Use scientific names of plants. Sampling Point: WC UPL ADSOlute uominant Inaicator Tree Stratum (Plot size: 30' ) % Cover Species? Status Dominance Test worksheet: 1. Pinus taeda 15 Yes FAC Number of Dominant Species 2. Acer rubrum 10 Yes FAC That Are OBL, FACW, or FAC: 2 (A) 3. Ilex opaca 5 No FACU Total Number of Dominant 4. Species Across All Strata: 8 (B) 5• Percent of Dominant Species 6. That Are OBL, FACW, or FAC: 25.0% (A/B) 7. Prevalence Index worksheet: 30 =Total Cover Total % Cover of: Multiply by: 50% of total cover: 15 20% of total cover: 6 OBL species 0 x 1 = 0 Sapling/Shrub Stratum (Plot size: 15' ) FACW species 0 x 2 = 0 1. Juniperus virginiana 5 Yes FACU FAC species 25 x 3 = 75 2. Ilex opaca 5 Yes FACU FACU species 35 x 4 = 140 3. Elaeagnus umbellata 5 Yes UPL UPL species 5 x 5 = 25 4. Column Totals: 65 (A) 240 (B) 5. Prevalence Index = B/A = 3.69 6. Hydrophytic Vegetation Indicators: 7. _ 1 - Rapid Test for Hydrophytic Vegetation 8. - Dominance Test is >50% 9. -2 3 - Prevalence Index is :53.0' 15 =Total Cover 4 - Morphological Adaptations' (Provide supporting 50% of total cover: 8 20% of total cover: 3 data in Remarks or on a separate sheet) Herb Stratum (Plot size: 5' ) -Problematic Hydrophytic Vegetation' (Explain) 1. Polystichum acrostichoides 15 Yes FACU 'Indicators of hydric soil and wetland hydrology must 2. Botrychium dissectum 5 Yes FAC be present, unless disturbed or problematic. Definitions of Four Vegetation Strata: 3. Hedera helix 5 Yes FACU 4• Tree - Woody plants, excluding vines, 3 in. (7.6 cm) or 5. more in diameter at breast height (DBH), regardless of 6 height. 7• 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. 25 =Total Cover Woody Vine - All woody vines greater than 3.28 ft in 50% of total cover: 13 20% of total cover: 5 height. Woody Vine Stratum (Plot size: 15' ) 1. 2. 3. 4. 5' Hydrophytic =Total Cover Vegetation 50% of total cover: 20% of total cover: Present? Yes No X Remarks: (Include photo numbers here or on a separate sheet.) US Army Corps of Engineers Eastern Mountains and Piedmont - Version 2.0 SOIL Sampling Point: WC UPL 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 0-3 10YR 3/3 100 Loamy/Clayey 3-12 10YR 4/4 100 Loamy/Clayey '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 Soils3: _ 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) 3Indicators 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: This data sheet is revised from Eastern Mountains and Piedmont Regional Supplement Version 2.0 to include the NRCS Field Indicators of Hydric Soils, Version 8.0, 2016. US Army Corps of Engineers Eastern Mountains and Piedmont — Version 2.0 WETLAND DETERMINATION DATA SHEET — Eastern Mountains and Piedmont Region Project/Site: EB-6038 City/County: Hickory, Catawba Sampling Date: 1/27/20 Applicant/Owner: City of Hickory, Jag Properties LLC and Summit Offices Owners Association State: NC Sampling Point: WC WET Investigator(s): Ryan Elliott Section, Township, Range: Hickory Landform (hillside, terrace, etc.): Basin Local relief (concave, convex, none): Concave Slope (%): 2 Subregion (LRR or MLRA): LRR P, MLRA 136 Lat: 35.748902 Long:-81.371372 Datum: WGS84 Soil Map Unit Name: FcC: Fairview gravelly fine sandy loam NWI classification: None 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 or Hydrology significantly disturbed? Are "Normal Circumstances" present? Yes No X 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 X No within a Wetland? Yes X No Wetland Hydrology Present? Yes X No Remarks: The data point is within a maintained field that is frequenty mowed. HYDROLOGY Wetland Hydrology Indicators: Secondary Indicators (minimum of two reguired) Primary Indicators (minimum of one is required; check all that apply) _Surface Soil Cracks (136) X Surface Water (A1) _True Aquatic Plants (1314) _Sparsely Vegetated Concave Surface (138) X High Water Table (A2) _ Hydrogen Sulfide Odor (Cl) —Drainage Patterns (1310) X Saturation (A3) -Oxidized Rhizospheres on Living Roots (C3) _ Moss Trim Lines (B16) —Water Marks (61) _ Presence of Reduced Iron (C4) _ Dry -Season Water Table (C2) —Sediment Deposits (132) _ Recent Iron Reduction in Tilled Soils (C6) —Crayfish Burrows (C8) _ Drift Deposits (133) —Thin Muck Surface (C7) X Saturation Visible on Aerial Imagery (C9) —Algal Mat or Crust (134) -Other (Explain in Remarks) —Stunted or Stressed Plants (D1) —Iron Deposits (135) _ Geomorphic Position (D2) _ Inundation Visible on Aerial Imagery (137) —Shallow Aquitard (D3) —Water-Stained Leaves (69) _ Microtopographic Relief (D4) Aquatic Fauna (1313) X FAC-Neutral Test (D5) Field Observations: Surface Water Present? Yes X No Depth (inches): 4 Water Table Present? Yes X No Depth (inches): 0 Saturation Present? Yes X No Depth (inches): 0 Wetland Hydrology Present? Yes X No (includes capillary fringe) Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: Remarks: US Army Corps of Engineers Eastern Mountains and Piedmont — Version 2.0 VEGETATION (Four Strata) - Use scientific names of plants. Sampling Point: WC WET Absolute Dominant Indicator Tree Stratum (Plot size: 30' ) % 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 0 x 1 = 0 Sapling/Shrub Stratum (Plot size: 15' ) FACW species 45 x 2 = 90 1. FAC species 0 x 3 = 0 2. FACU species 0 x 4 = 0 3. UPL species 10 x 5 = 50 4. Column Totals: 55 (A) 140 (B) 5. Prevalence Index = B/A = 2.55 6. Hydrophytic Vegetation Indicators: 7. _ 1 - Rapid Test for Hydrophytic Vegetation 8. X 2 - Dominance Test is >50% 9. X 3 - Prevalence Index is :53.0' =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' ) -Problematic Hydrophytic Vegetation' (Explain) 1. Juncus effusus 30 Yes FACW 'Indicators of hydric soil and wetland hydrology must be 2. Cyperus odoratus 15 Yes FACW present, unless disturbed or problematic. Definitions of Four Vegetation Strata: 3. Danthonia spicata 10 No UPL 4• Tree - Woody plants, excluding vines, 3 in. (7.6 cm) or 5• more in diameter at breast height (DBH), regardless of 6 height. 7• 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. 55 =Total Cover Woody Vine - All woody vines greater than 3.28 ft in 50% of total cover: 28 20% of total cover: 11 height. Woody Vine Stratum (Plot size: 15, ) 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.) The field that contains this wetland had been cut somewhat recently, likely at the end of the 2019 growing season. Aerial imagery indicates that the field has been maintained for more than 15 years. US Army Corps of Engineers Eastern Mountains and Piedmont - Version 2.0 SOIL Sampling Point: WC WET 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) % Types Loc2 Texture Remarks 0-3 10YR 5/2 100 Loamy/Clayey 3-12 7.5YR 4/6 70 10YR 5/4 20 C M Loamy/Clayey Distinct redox concentrations 2.5YR 4/6 10 C M Faint redox concentrations '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 Soils3: _ 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) X 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) 3Indicators 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 X No Remarks: This data sheet is revised from Eastern Mountains and Piedmont Regional Supplement Version 2.0 to include the NRCS Field Indicators of Hydric Soils, Version 8.0, 2016. US Army Corps of Engineers Eastern Mountains and Piedmont — Version 2.0 WETLAND DETERMINATION DATA SHEET — Eastern Mountains and Piedmont Region Project/Site: EB-6038 City/County: Hickory, Catawba Sampling Date: 1/27/20 Applicant/Owner: City of Hickory, City of Hickory State: NC Sampling Point: WD UPL Investigator(s): Ryan Elliott Section, Township, Range: Hickory Landform (hillside, terrace, etc.): Hillslope Local relief (concave, convex, none): Convex Slope (%): 10 Subregion (LRR or MLRA): LRR P, MLRA 136 Lat: 35.744093 Long:-81.386461 Datum: WGS84 Soil Map Unit Name: Udorthents NWI classification: None Are climatic / hydrologic conditions on the site typical for this time of year? Yes X No (If no, explain in Remarks.) Are Vegetation Soil or Hydrology significantly disturbed? Are "Normal Circumstances" present? Yes X No Are Vegetation X 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 No X Is the Sampled Area Hydric Soil Present? Yes No X within a Wetland? Yes No X Wetland Hydrology Present? Yes X No Remarks: Invasive Ligustrum sinense was identified in the surrounding area 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 (A1) —True Aquatic Plants (1314) _Sparsely Vegetated Concave Surface (138) _ High Water Table (A2) _ Hydrogen Sulfide Odor (Cl) —Drainage Patterns (1310) X Saturation (A3) -Oxidized Rhizospheres on Living Roots (C3) _ Moss Trim Lines (B16) —Water Marks (61) _ Presence of Reduced Iron (C4) _ Dry -Season Water Table (C2) —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) _ Geomorphic Position (D2) _ Inundation Visible on Aerial Imagery (137) —Shallow Aquitard (D3) —Water-Stained Leaves (69) _ 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 X No Depth (inches): 0 Wetland Hydrology Present? Yes X No (includes capillary fringe) Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: Remarks: Presence of hydrology is likely due to rainfall events prior to the visit. US Army Corps of Engineers Eastern Mountains and Piedmont — Version 2.0 VEGETATION (Four Strata) - Use scientific names of plants. Sampling Point: WD UPL Absolute Dominant Indicator Tree Stratum (Plot size: 30' ) % Cover Species? Status Dominance Test worksheet: 1. Pinus taeda 15 Yes FAC Number of Dominant Species 2. Acer rubrum 10 Yes FAC That Are OBL, FACW, or FAC: 3 (A) 3. Fagus grandifolia 10 Yes FACU Total Number of Dominant 4. Species Across All Strata: 7 (B) 5• Percent of Dominant Species 6. That Are OBL, FACW, or FAC: 42.9% (A/B) 7. Prevalence Index worksheet: 35 =Total Cover Total % Cover of: Multiply by: 50% of total cover: 18 20% of total cover: 7 OBL species 0 x 1 = 0 Sapling/Shrub Stratum (Plot size: 15' ) FACW species 0 x 2 = 0 1. Ligustrum sinense 15 Yes FACU FAC species 30 x 3 = 90 2. Ilex opaca 10 Yes FACU FACU species 40 x 4 = 160 3. UPL species 0 x 5 = 0 4. Column Totals: 70 (A) 250 (B) 5. Prevalence Index = B/A = 3.57 6. Hydrophytic Vegetation Indicators: 7. _ 1 - Rapid Test for Hydrophytic Vegetation 8. - Dominance Test is >50% 9. -2 3 Prevalence Index is :53.0' 25 =Total Cover 4 - Morphological Adaptations' (Provide supporting 50% of total cover: 13 20% of total cover: 5 data in Remarks or on a separate sheet) Herb Stratum (Plot size: 5' ) -Problematic Hydrophytic Vegetation' (Explain) 1 'Indicators of hydric soil and wetland hydrology must be 2. present, unless disturbed or problematic. Definitions of Four Vegetation Strata: 3. 4• Tree - Woody plants, excluding vines, 3 in. (7.6 cm) or 5, more in diameter at breast height (DBH), regardless of 6 height. 7• 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. =Total Cover Woody Vine - All woody vines greater than 3.28 ft in 50% of total cover: 20% of total cover: height. Woody Vine Stratum (Plot size: 15, ) 1. Lonicera japonica 5 Yes FACU 2. Toxicodendron radicans 5 Yes FAC 3. 4. 5. Hydrophytic 10 =Total Cover Vegetation 50% of total cover: 5 20% of total cover: 2 Present? Yes No X Remarks: (Include photo numbers here or on a separate sheet.) US Army Corps of Engineers Eastern Mountains and Piedmont - Version 2.0 SOIL Sampling Point: WD UPL 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) % Types Loc2 Texture Remarks 0-2 10YR 4/3 100 Loamy/Clayey 2-12 7.5YR 4/4 80 10YR 4/4 20 C M Loamy/Clayey Faint redox concentrations '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 Soils3: _ 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) 3Indicators 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: This data sheet is revised from Eastern Mountains and Piedmont Regional Supplement Version 2.0 to include the NRCS Field Indicators of Hydric Soils, Version 8.0, 2016. US Army Corps of Engineers Eastern Mountains and Piedmont — Version 2.0 WETLAND DETERMINATION DATA SHEET — Eastern Mountains and Piedmont Region Project/Site: EB-6038 City/County: Hickory, Catawba Sampling Date: 1/27/20 Applicant/Owner: City of Hickory, City of Hickory State: NC Sampling Point: WD WET Investigator(s): Ryan Elliott Section, Township, Range: Hickory Landform (hillside, terrace, etc.): Basin Local relief (concave, convex, none): Concave Slope (%): 3 Subregion (LRR or MLRA): LRR P, MLRA 136 Lat: 35.744113 Long:-81.386448 Datum: WGS84 Soil Map Unit Name: Udorthents NWI classification: None Are climatic / hydrologic conditions on the site typical for this time of year? Yes X No (If no, explain in Remarks.) Are Vegetation Soil or Hydrology significantly disturbed? Are "Normal Circumstances" present? Yes X No Are Vegetation X 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 X No Wetland Hydrology Present? Yes X No Remarks: Invasive Ligustrum sinense was identified in the surrounding area Soils were too loose to walk on and may have had redox in inaccessible 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) X Surface Water (A1) _True Aquatic Plants (1314) _Sparsely Vegetated Concave Surface (138) X High Water Table (A2) _ Hydrogen Sulfide Odor (Cl) X Drainage Patterns (610) X Saturation (A3) -Oxidized Rhizospheres on Living Roots (C3) _ Moss Trim Lines (B16) —Water Marks (61) _ Presence of Reduced Iron (C4) _ Dry -Season Water Table (C2) —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) X Other (Explain in Remarks) —Stunted or Stressed Plants (D1) —Iron Deposits (135) _ Geomorphic Position (D2) _ Inundation Visible on Aerial Imagery (137) —Shallow Aquitard (D3) X Water -Stained Leaves (69) _ Microtopographic Relief (D4) Aquatic Fauna (1313) FAC-Neutral Test (D5) Field Observations: Surface Water Present? Yes X No Depth (inches): 2 Water Table Present? Yes X No Depth (inches): 0 Saturation Present? Yes X No Depth (inches): 0 Wetland Hydrology Present? Yes X No (includes capillary fringe) Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: Remarks: Iron oxidizing bacteria were present. US Army Corps of Engineers Eastern Mountains and Piedmont — Version 2.0 VEGETATION (Four Strata) - Use scientific names of plants. Sampling Point: WD WET Absolute Dominant Indicator Tree Stratum (Plot size: 30' ) % Cover Species? Status Dominance Test worksheet: 1. Acer rubrum 10 Yes FAC Number of Dominant Species 2. That Are OBL, FACW, or FAC: 5 (A) 3. Total Number of Dominant 4. Species Across All Strata: 9 (B) 5. Percent of Dominant Species 6. That Are OBL, FACW, or FAC: 55.6% (A/B) 7. Prevalence Index worksheet: 10 =Total Cover Total % Cover of: Multiply by: 50% of total cover: 5 20% of total cover: 2 OBL species 0 x 1 = 0 Sapling/Shrub Stratum (Plot size: 15' ) FACW species 0 x 2 = 0 1. Ilex opaca 10 Yes FACU FAC species 35 x 3 = 105 2. Ligustrum sinense 10 Yes FACU FACU species 30 x 4 = 120 3. UPL species 0 x 5 = 0 4. Column Totals: 65 (A) 225 (B) 5. Prevalence Index = B/A = 3.46 6. Hydrophytic Vegetation Indicators: 7. _ 1 - Rapid Test for Hydrophytic Vegetation 8. X 2 - Dominance Test is >50% 9. 3 Prevalence Index is :53.0' 20 =Total Cover 4 - Morphological Adaptations' (Provide supporting 50% of total cover: 10 20% of total cover: 4 data in Remarks or on a separate sheet) Herb Stratum (Plot size: 5' ) -Problematic Hydrophytic Vegetation' (Explain) 1. Toxicodendron radicans 10 Yes FAC 'Indicators of hydric soil and wetland hydrology must be 2. Ligustrum sinense 5 Yes FACU present, unless disturbed or problematic. Definitions of Four Vegetation Strata: 3. Smilax rotundifolia 5 Yes FAC 4• Tree - Woody plants, excluding vines, 3 in. (7.6 cm) or 5• more in diameter at breast height (DBH), regardless of 6 height. 7• 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. 20 =Total Cover Woody Vine - All woody vines greater than 3.28 ft in 50% of total cover: 10 20% of total cover: 4 height. Woody Vine Stratum (Plot size: 15, ) 1. Toxicodendron radicans 5 Yes FAC 2. Lonicera japonica 5 Yes FACU 3. Smilax rotundifolia 5 Yes FAC 4. 5. Hydrophytic 15 =Total Cover Vegetation 50% of total cover: 8 20% of total cover: 3 Present? Yes X No Remarks: (Include photo numbers here or on a separate sheet.) A patch of invasive Pyrus calleryana seems to have spread significantly into the wetland as compared to aerial imagery from March of 2018 US Army Corps of Engineers Eastern Mountains and Piedmont - Version 2.0 SOIL Sampling Point: WD WET 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) % Types Loc2 Texture Remarks 0-12 10YR 2/2 100 Loamy/Clayey 'Type: C=Concentration, D=Depletion, 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): 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) _ 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 Soils3: 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 No X Remarks: This data sheet is revised from Eastern Mountains and Piedmont Regional Supplement Version 2.0 to include the NRCS Field Indicators of Hydric Soils, Version 8.0, 2016. Soils appeared to be depleted, but no redox or oxidized rhizospheres were observed. Soils were too loose to walk on and may have had redox in inaccessible areas. US Army Corps of Engineers Eastern Mountains and Piedmont — Version 2.0 WETLAND DETERMINATION DATA SHEET — Eastern Mountains and Piedmont Region Project/Site: EB-6038 City/County: Hickory, Catawba Sampling Date: 1/27/20 Applicant/Owner: City of Hickory, City of Hickory State: NC Sampling Point: WE UPL Investigator(s): Ryan Elliott Section, Township, Range: Hickory Landform (hillside, terrace, etc.): Hillslope Local relief (concave, convex, none): Convex Slope (%): 6 Subregion (LRR or MLRA): LRR P, MLRA 136 Lat: 35.744082 Long:-81.386548 Datum: WGS84 Soil Map Unit Name: Udorthents NWI classification: None Are climatic / hydrologic conditions on the site typical for this time of year? Yes X No (If no, explain in Remarks.) Are Vegetation Soil or Hydrology significantly disturbed? Are "Normal Circumstances" present? Yes X No Are Vegetation X 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 No X Is the Sampled Area Hydric Soil Present? Yes No X within a Wetland? Yes No X Wetland Hydrology Present? Yes X No Remarks: Invasive Ligustrum sinense was identified in the surrounding area 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 (A1) _True Aquatic Plants (1314) _Sparsely Vegetated Concave Surface (138) _ High Water Table (A2) _ Hydrogen Sulfide Odor (Cl) —Drainage Patterns (1310) X Saturation (A3) -Oxidized Rhizospheres on Living Roots (C3) _ Moss Trim Lines (B16) —Water Marks (61) _ Presence of Reduced Iron (C4) _ Dry -Season Water Table (C2) —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) _ Geomorphic Position (D2) _ Inundation Visible on Aerial Imagery (137) —Shallow Aquitard (D3) —Water-Stained Leaves (69) _ 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 X No Depth (inches): 0 Wetland Hydrology Present? Yes X No (includes capillary fringe) Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: Remarks: Presence of hydrology is likely due to rainfall events prior to the visit. US Army Corps of Engineers Eastern Mountains and Piedmont — Version 2.0 VEGETATION (Four Strata) - Use scientific names of plants. Sampling Point: WE UPL Absolute Dominant Indicator Tree Stratum (Plot size: 30' ) % Cover Species? Status Dominance Test worksheet: 1. Platanus occidentalis 10 Yes FACW Number of Dominant Species 2. Fagus grandifolia 10 Yes FACU That Are OBL, FACW, or FAC: 2 (A) 3. Total Number of Dominant 4. Species Across All Strata: 5 (B) 5. Percent of Dominant Species 6. That Are OBL, FACW, or FAC: 40.0% (A/B) 7. Prevalence Index worksheet: 20 =Total Cover Total % Cover of: Multiply by: 50% of total cover: 10 20% of total cover: 4 OBL species 0 x 1 = 0 Sapling/Shrub Stratum (Plot size: 15' ) FACW species 10 x 2 = 20 1. Fagus grandifolia 10 Yes FACU FAC species 5 x 3 = 15 2. Ligustrum sinense 10 Yes FACU FACU species 30 x 4 = 120 3. Acer rubrum 5 Yes FAC UPL species 0 x 5 = 0 4. Column Totals: 45 (A) 155 (B) 5. Prevalence Index = B/A = 3.44 6. Hydrophytic Vegetation Indicators: 7. _ 1 - Rapid Test for Hydrophytic Vegetation 8. - Dominance Test is >50% 9. -2 3 Prevalence Index is :53.0' 25 =Total Cover 4 - Morphological Adaptations' (Provide supporting 50% of total cover: 13 20% of total cover: 5 data in Remarks or on a separate sheet) Herb Stratum (Plot size: 15, ) -Problematic Hydrophytic Vegetation' (Explain) 1 'Indicators of hydric soil and wetland hydrology must be 2. present, unless disturbed or problematic. Definitions of Four Vegetation Strata: 3. 4• Tree - Woody plants, excluding vines, 3 in. (7.6 cm) or 5, more in diameter at breast height (DBH), regardless of 6 height. 7• 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. =Total Cover Woody Vine - All woody vines greater than 3.28 ft in 50% of total cover: 20% of total cover: height. Woody Vine Stratum (Plot size: 15, ) 1. 2. 3. 4. 5. Hydrophytic =Total Cover Vegetation 50% of total cover: 20% of total cover: Present? Yes No X Remarks: (Include photo numbers here or on a separate sheet.) US Army Corps of Engineers Eastern Mountains and Piedmont - Version 2.0 SOIL Sampling Point: WE UPL 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) % Types Loc2 Texture Remarks 0-3 7.5YR 4/3 100 Loamy/Clayey 3-12 2.5YR 4/6 75 7.5YR 4/3 15 C M Loamy/Clayey Prominent redox concentrations '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 Soils3: _ 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) 3Indicators 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: This data sheet is revised from Eastern Mountains and Piedmont Regional Supplement Version 2.0 to include the NRCS Field Indicators of Hydric Soils, Version 8.0, 2016. US Army Corps of Engineers Eastern Mountains and Piedmont — Version 2.0 WETLAND DETERMINATION DATA SHEET — Eastern Mountains and Piedmont Region Project/Site: EB-6038 City/County: Hickory, Catawba Sampling Date: 1/27/20 Applicant/Owner: City of Hickory, City of Hickory State: NC Sampling Point: WE WET Investigator(s): Ryan Elliott Section, Township, Range: Hickory Landform (hillside, terrace, etc.): Basin Local relief (concave, convex, none): Concave Slope (%): 3 Subregion (LRR or MLRA): LRR P, MLRA 136 Lat: 35.744136 Long:-81.386558 Datum: WGS84 Soil Map Unit Name: Udorthents NWI classification: None Are climatic / hydrologic conditions on the site typical for this time of year? Yes X No (If no, explain in Remarks.) Are Vegetation Soil or Hydrology significantly disturbed? Are "Normal Circumstances" present? Yes X No Are Vegetation X 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 X No within a Wetland? Yes X No Wetland Hydrology Present? Yes X No Remarks: Invasive Ligustrum sinense was identified in the surrounding area 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) X Surface Water (A1) _True Aquatic Plants (1314) _Sparsely Vegetated Concave Surface (138) X High Water Table (A2) _ Hydrogen Sulfide Odor (Cl) X Drainage Patterns (610) X Saturation (A3) -Oxidized Rhizospheres on Living Roots (C3) _ Moss Trim Lines (B16) —Water Marks (61) _ Presence of Reduced Iron (C4) _ Dry -Season Water Table (C2) —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) _ Geomorphic Position (D2) _ Inundation Visible on Aerial Imagery (137) —Shallow Aquitard (D3) X Water -Stained Leaves (69) _ Microtopographic Relief (D4) Aquatic Fauna (1313) FAC-Neutral Test (D5) Field Observations: Surface Water Present? Yes X No Depth (inches): 1 Water Table Present? Yes X No Depth (inches): 0 Saturation Present? Yes X No Depth (inches): 0 Wetland Hydrology Present? Yes X No (includes capillary fringe) Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: Remarks: Iron oxidizing bacteria were very prevalant. US Army Corps of Engineers Eastern Mountains and Piedmont — Version 2.0 VEGETATION (Four Strata) - Use scientific names of plants. Sampling Point: WE WET Absolute Dominant Indicatc Tree Stratum (Plot size: 30' ) % Cover Species? Status 1. Acer rubrum 10 Yes FAC 2. Fagus grandifolia 5 Yes FACU 3. 4. 5. 6. 7. 15 =Total Cover 50% of total cover: 8 20% of total cover: 3 Sapling/Shrub Stratum (Plot size: 15' ) 1. Ligustrum sinense 15 Yes FACU 2. Ilex opaca 5 Yes FACU 3. 4. 5. 6. 7. 8. 9. 20 =Total Cover 50% of total cover: 10 20% of total cover: 4 Herb Stratum (Plot size: 5' ) 1. Smilax rotundifolia 5 Yes FAC 2. Toxicodendron radicans 5 Yes FAC 3. 4. 5. 6. 7. 8. 9. 10. 11. 10 =Total Cover 50% of total cover: 5 20% of total cover: 2 Woody Vine Stratum (Plot size: 15, ) 1. Toxicodendron radicans 5 Yes FAC 2. Smilax rotundifolia 5 Yes FAC 3. 4. 5. Dominance Test worksheet: Number of Dominant Species That Are OBL, FACW, or FAC: 5 (A) Total Number of Dominant Species Across All Strata: 8 (B) Percent of Dominant Species That Are OBL, FACW, or FAC: 62.5% (A/B) Prevalence Index worksheet: Total % Cover of: Multiply by: OBL species 0 x 1 = 0 FACW species 0 x 2 = 0 FAC species 30 x 3 = 90 FACU species 25 x 4 = 100 UPL species 0 x 5 = 0 Column Totals: 55 (A) 190 (B) Prevalence Index = B/A = 3.45 _ 1 - Rapid Test for Hydrophytic Vegetation X 2 - Dominance Test is >50% -3 Prevalence Index is :53.0' 4 - Morphological Adaptations' (Provide supporting data in Remarks or on a separate sheet) Problematic Hydrophytic Vegetation' (Explain) 'Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Definitions of Four Vegetation Strata: Tree - Woody plants, excluding vines, 3 in. (7.6 cm) or more in diameter at breast height (DBH), regardless of height. Sapling/Shrub - Woody plants, excluding vines, less than 3 in. DBH and greater than or equal to 3.28 ft (1 m) tall. Herb - All herbaceous (non -woody) plants, regardless of size, and woody plants less than 3.28 ft tall. Woody Vine - All woody vines greater than 3.28 ft in height. Hydrophytic 10 =Total Cover Vegetation 50% of total cover: 5 20% of total cover: 2 1 Present? Yes X No Remarks: (Include photo numbers here or on a separate sheet.) A patch of invasive Pyrus calleryana seems to have spread significantly into the wetland as compared to aerial imagery from March of 2018 US Army Corps of Engineers Eastern Mountains and Piedmont - Version 2.0 SOIL Sampling Point: WE WET 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) % Types Loc2 Texture Remarks 0-12 10YR 5/2 80 10YR 5/6 15 C M Loamy/Clayey Prominent redox concentrations 'Type: C=Concentration, D=Depletion, 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): 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) X 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 Soils3: 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 Remarks: This data sheet is revised from Eastern Mountains and Piedmont Regional Supplement Version 2.0 to include the NRCS Field Indicators of Hydric Soils, Version 8.0, 2016. US Army Corps of Engineers Eastern Mountains and Piedmont — Version 2.0 WETLAND DETERMINATION DATA SHEET — Eastern Mountains and Piedmont Region Project/Site: EB-6038 City/County: Hickory, Catawba Sampling Date: 2/25/20 Applicant/Owner: City of Hickory, City of Hickory State: NC Sampling Point: WF UPL Investigator(s): Ryan Elliott Section, Township, Range: Hickory Landform (hillside, terrace, etc.): Hillslope Local relief (concave, convex, none): Convex Slope (%): 4 Subregion (LRR or MLRA): LRR P, MLRA 136 Lat: 35.745528 Long:-81.381377 Datum: WGS84 Soil Map Unit Name: Udorthents NWI classification: None Are climatic / hydrologic conditions on the site typical for this time of year? Yes X No (If no, explain in Remarks.) Are Vegetation Soil or Hydrology 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 No X Is the Sampled Area Hydric Soil Present? Yes No X within a Wetland? Yes No X Wetland Hydrology Present? Yes X No Remarks: 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 (A1) _True Aquatic Plants (1314) _Sparsely Vegetated Concave Surface (138) _ High Water Table (A2) _ Hydrogen Sulfide Odor (Cl) —Drainage Patterns (1310) X Saturation (A3) -Oxidized Rhizospheres on Living Roots (C3) _ Moss Trim Lines (B16) —Water Marks (61) _ Presence of Reduced Iron (C4) _ Dry -Season Water Table (C2) —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) _ Geomorphic Position (D2) _ Inundation Visible on Aerial Imagery (137) —Shallow Aquitard (D3) —Water-Stained Leaves (69) _ 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 X No Depth (inches): 0 Wetland Hydrology Present? Yes X No (includes capillary fringe) Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: Remarks: Presence of hydrology is likely due to rainfall events prior to the visit. US Army Corps of Engineers Eastern Mountains and Piedmont — Version 2.0 VEGETATION (Four Strata) - Use scientific names of plants. Sampling Point: WF UPL Absolute Dominant Indicator Tree Stratum (Plot size: 30' ) % Cover Species? Status Dominance Test worksheet: 1. Acer rubrum 10 Yes FAC Number of Dominant Species 2. Quercus talcata 5 Yes FACU That Are OBL, FACW, or FAC: 3 (A) 3. Ilex opaca 5 Yes FACU Total Number of Dominant 4. Species Across All Strata: 8 (B) 5. Percent of Dominant Species 6. That Are OBL, FACW, or FAC: 37.5% (A/B) 7. Prevalence Index worksheet: 20 =Total Cover Total % Cover of: Multiply by: 50% of total cover: 10 20% of total cover: 4 OBL species 0 x 1 = 0 Sapling/Shrub Stratum (Plot size: 15' ) FACW species 0 x 2 = 0 1. Acer rubrum 5 Yes FAC FAC species 20 x 3 = 60 2. Acer negundo 5 Yes FAC FACU species 25 x 4 = 100 3. Ilex opaca 5 Yes FACU UPL species 60 x 5 = 300 4. Column Totals: 105 (A) 460 (B) 5. Prevalence Index = B/A = 4.38 6. Hydrophytic Vegetation Indicators: 7. _ 1 - Rapid Test for Hydrophytic Vegetation 8. - Dominance Test is >50% 9. -2 3 Prevalence Index is :53.0' 15 =Total Cover 4 - Morphological Adaptations' (Provide supporting 50% of total cover: 8 20% of total cover: 3 data in Remarks or on a separate sheet) Herb Stratum (Plot size: 15, ) -Problematic Hydrophytic Vegetation' (Explain) 1. Diphasiastrum digitatum 60 Yes UPL 'Indicators of hydric soil and wetland hydrology must be 2. Polystichum acrostichoides 5 No FACU present, unless disturbed or problematic. Definitions of Four Vegetation Strata: 3. 4• Tree - Woody plants, excluding vines, 3 in. (7.6 cm) or 5, more in diameter at breast height (DBH), regardless of 6 height. 7• 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. 65 =Total Cover Woody Vine - All woody vines greater than 3.28 ft in 50% of total cover: 33 20% of total cover: 13 height. Woody Vine Stratum (Plot size: 15, ) 1. Lonicera japonica 5 Yes FACU 2. 3. 4. 5. Hydrophytic 5 =Total Cover Vegetation 50% of total cover: 3 20% of total cover: 1 Present? Yes No X Remarks: (Include photo numbers here or on a separate sheet.) US Army Corps of Engineers Eastern Mountains and Piedmont - Version 2.0 SOIL Sampling Point: WF UPL 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) % Types Loc2 Texture Remarks 0-3 10YR 5/4 60 5YR 5/6 40 C M Loamy/Clayey Prominent redox concentrations 3-6 7.5YR 3/4 100 Loamy/Clayey 6-12 5YR 4/4 100 Loamy/Clayey '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 Soils3: _ 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) 3Indicators 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: This data sheet is revised from Eastern Mountains and Piedmont Regional Supplement Version 2.0 to include the NRCS Field Indicators of Hydric Soils, Version 8.0, 2016. US Army Corps of Engineers Eastern Mountains and Piedmont — Version 2.0 WETLAND DETERMINATION DATA SHEET — Eastern Mountains and Piedmont Region Project/Site: EB-6038 City/County: Hickory, Catawba Sampling Date: 2/25/20 Applicant/Owner: City of Hickory, City of Hickory State: NC Sampling Point: WF WET Investigator(s): Ryan Elliott Section, Township, Range: Hickory Landform (hillside, terrace, etc.): Basin Local relief (concave, convex, none): Concave Slope (%): 2 Subregion (LRR or MLRA): LRR P, MLRA 136 Lat: 35.745545 Long:-81.381395 Datum: WGS84 Soil Map Unit Name: Udorthents NWI classification: None Are climatic / hydrologic conditions on the site typical for this time of year? Yes X No (If no, explain in Remarks.) Are Vegetation Soil or Hydrology 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 X No within a Wetland? Yes X No Wetland Hydrology Present? Yes X No Remarks: Spagnum moss was prevelant within the area 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) X Surface Water (A1) _True Aquatic Plants (1314) _Sparsely Vegetated Concave Surface (138) X High Water Table (A2) _ Hydrogen Sulfide Odor (Cl) —Drainage Patterns (1310) X Saturation (A3) X Oxidized Rhizospheres on Living Roots (C3) _ Moss Trim Lines (B16) —Water Marks (61) _ Presence of Reduced Iron (C4) _ Dry -Season Water Table (C2) —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) _ Geomorphic Position (D2) _ Inundation Visible on Aerial Imagery (137) —Shallow Aquitard (D3) X Water -Stained Leaves (69) _ Microtopographic Relief (D4) Aquatic Fauna (1313) X FAC-Neutral Test (D5) Field Observations: Surface Water Present? Yes X No Depth (inches): 3 Water Table Present? Yes X No Depth (inches): 0 Saturation Present? Yes X No Depth (inches): 0 Wetland Hydrology Present? Yes X No (includes capillary fringe) Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: Remarks: US Army Corps of Engineers Eastern Mountains and Piedmont — Version 2.0 VEGETATION (Four Strata) - Use scientific names of plants. Sampling Point: WF WET Absolute Dominant Indicator Tree Stratum (Plot size: 30' ) % Cover Species? Status Dominance Test worksheet: 1 Number of Dominant Species 2. That Are OBL, FACW, or FAC: 3 (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: 75.0% (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: 15' ) FACW species 50 x 2 = 100 1. Acer negundo 5 Yes FAC FAC species 5 x 3 = 15 2. FACU species 0 x 4 = 0 3. UPL species 5 x 5 = 25 4. Column Totals: 60 (A) 140 (B) 5. Prevalence Index = B/A = 2.33 6. Hydrophytic Vegetation Indicators: 7. _ 1 - Rapid Test for Hydrophytic Vegetation 8. X 2 - Dominance Test is >50% 9. X 3 - Prevalence Index is :53.0' 5 =Total Cover 4 - Morphological Adaptations' (Provide supporting 50% of total cover: 3 20% of total cover: 1 data in Remarks or on a separate sheet) Herb Stratum (Plot size: 5' ) -Problematic Hydrophytic Vegetation' (Explain) 1. Cyperus odoratus 40 Yes FACW 'Indicators of hydric soil and wetland hydrology must be 2. Juncus effusus 10 Yes FACW present, unless disturbed or problematic. Definitions of Four Vegetation Strata: 3. 4• Tree - Woody plants, excluding vines, 3 in. (7.6 cm) or 5• more in diameter at breast height (DBH), regardless of 6 height. 7• 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. 50 =Total Cover Woody Vine - All woody vines greater than 3.28 ft in 50% of total cover: 25 20% of total cover: 10 height. Woody Vine Stratum (Plot size: 15, ) 1. Polygonum sagittatum 5 Yes UPL 2. 3. 4. 5. Hydrophytic 5 =Total Cover Vegetation 50% of total cover: 3 20% of total cover: 1 Present? Yes X No Remarks: (Include photo numbers here or on a separate sheet.) US Army Corps of Engineers Eastern Mountains and Piedmont - Version 2.0 SOIL Sampling Point: WF WET 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) % Types Loc2 Texture Remarks 0-4 10YR 4/2 85 5YR 5/6 15 C M Loamy/Clayey Distinct redox concentrations 4-12 10YR 3/2 60 5YR 4/6 40 C M Loamy/Clayey Distinct redox concentrations '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 Soils3: _ 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) X Depleted Matrix (F3) (MLRA 136, 147) _ 2 cm Muck (A10) (LRR N) X 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) X 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) 3Indicators 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 X No Remarks: This data sheet is revised from Eastern Mountains and Piedmont Regional Supplement Version 2.0 to include the NRCS Field Indicators of Hydric Soils, Version 8.0, 2016. US Army Corps of Engineers Eastern Mountains and Piedmont — Version 2.0 NC WAM FIELD ASSESSMENT FORM Accompanies user manuai version am USACE AID # NCDWR# Project Name EB-6038 Date of Evaluation 1/14/20 Applicant/Owner Name City of Hickory, Outbox Hickory LLC Wetland Site Name WA Wetland Type Basin Wetland Assessor Name/Organization Ran Elliott / TGS Engineers Level III Ecoregion Piedmont Nearest Named Water Body Catawba River River Basin Catawba USGS 8-Digit Catalogue Unit 03050101 County Catawba NCDWR Region Mooresville ® Yes ❑ No Precipitation within 48 hrs? Latitude/Longitude (deci-degrees) 35.748926,-81.373102 Evidence of stressors affecting the assessment area (may not be within the assessment area) Please circle and/or make note on the last page 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 Regulatory Considerations - Were regulatory considerations evaluated? ®Yes ❑No If Yes, check all that apply to the assessment area. ❑ Anadromous fish ❑ Federally protected species or State endangered or threatened species ® NCDWR 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 Does the assessment area experience overbank flooding during normal rainfall conditions? ❑ 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], hydrologic alteration) 2. 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. 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). 3. Water Storage/Surface Relief —assessment area/wetland type condition metric (skip for all marshes) Check a box in each column. Select the appropriate storage for the assessment area (AA) and the wetland type (WT). AA WT 3a. ❑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 3b. ❑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 (skip for all marshes) 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. 4a. ❑A Sandy soil ®B Loamy or clayey soils exhibiting redoximorphic features (concentrations, depletions, or rhizospheres) ❑C Loamy or clayey soils not exhibiting redoximorphic features ❑D Loamy or clayey gleyed soil ❑E Histosol or histic epipedon 4b. ❑A Soil ribbon < 1 inch ®B Soil ribbon >_ 1 inch 4c. ®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) 6. Land Use — opportunity metric (skip for non -riparian wetlands) Check all that apply (at least one box in each column). Evaluation involves a GIS effort with field adjustment. Consider sources draining to assessment area within entire upstream watershed (WS), within 5 miles and within the watershed draining to the assessment area (5M), and within 2 miles and within the watershed draining to the assessment area (2M). WS 5M 2M ❑A ❑A ❑A > 10% impervious surfaces ❑B ❑B ❑B Confined animal operations (or other local, concentrated source of pollutants ❑C ❑C ❑C >_ 20% coverage of pasture ❑D ❑D ❑D >_ 20% coverage of agricultural land (regularly plowed land) ❑E ❑E ❑E >_ 20% coverage of maintained grass/herb ❑F ❑F ❑F >_ 20% coverage of clear-cut land ❑G ❑G ❑G Little or no opportunity to improve water quality. Lack of opportunity may result from little or no disturbance in the watershed or hydrologic alterations that prevent drainage and/or overbank flow from affecting the assessment area. 7. Wetland Acting as Vegetated Buffer— assessment area/wetland complex condition metric (skip for non -riparian wetlands) 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? (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.) ❑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. 05 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. El 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 (evaluate WT for all marshes and Estuarine Woody Wetland only; evaluate WC for Bottomland Hardwood Forest, Headwater Forest, and Riverine Swamp Forest only) Check a box in each column for riverine wetlands only. Select the average 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 (skip for non -riparian wetlands) Answer for assessment area dominant landform. ❑A Evidence of short -duration inundation (< 7 consecutive days) ❑B Evidence of saturation, without evidence of inundation El 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 (skip for non -riparian wetlands and all marshes) 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 El El El 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, regularly maintained utility line corridors the width of a four -lane road or wider, 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 (skip for all marshes and Estuarine Woody Wetland) May involve a GIS effort with field adjustment. Estimate distance from wetland type boundary to artificial edges. Artificial edges include non -forested areas >_ 40 feet wide such as fields, development, roads, regularly maintained utility line corridors, and clear -cuts. Consider the eight main points of the compass. Artificial edge occurs within 150 feet in how many directions? If the assessment area is clear cut, select option "C." ❑A 0 ❑B 1 to 4 ®C 5to8 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, or expected species are unnaturally absent (planted stands of non - characteristic species or at least one stratum inappropriately composed of a single species), or exotic species are dominant in at least one stratum. 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 assessment area 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 o ❑A ❑A Canopy closed, or nearly closed, with natural gaps associated with natural processes ❑B ❑B Canopy present, but opened more than natural gaps U ®C ®C Canopy sparse or absent >, o ❑A ❑A Dense mid-story/sapling layer co ®B ®B Moderate density mid-story/sapling layer ❑C ❑C Mid-story/sapling layer sparse or absent ❑A ❑A Dense shrub layer .L ®B ®B Moderate density shrub layer u) ❑C ❑C Shrub layer sparse or absent .fl ®A ®A Dense herb layer _ ❑B ❑B Moderate density herb layer ❑C ❑C Herb layer sparse or absent 18. Snags — wetland type condition metric (skip for all marshes) ❑A Large snags (more than one) are visible (> 12 inches DBH, or large relative to species present and landscape stability). ®B Not A 19. Diameter Class Distribution — wetland type condition metric (skip for all marshes) ❑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 (skip for all marshes) 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 Not 21. Vegetation/Open Water Dispersion — wetland type/open water condition metric (evaluate for Non -Tidal Freshwater Marsh only) Select the figure that best describes the amount of interspersion between vegetation and open water in the growing season. Patterned areas indicate vegetated areas, while solid white areas indicate open water. ❑A ❑B ❑C ❑D N PP 1 ^ 22. Hydrologic Connectivity — assessment area condition metric (evaluate for riparian wetlands and Salt/Brackish Marsh 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. Documentation required if evaluated as B, C, or D. ❑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 NC WAM Wetland Rating Sheet Accompanies User Manual Version 5.0 Wetland Site Name WA Date of Assessment 1/14/20 Wetland Type Basin Wetland Ryan Elliott / TGS Assessor Name/Organization Engineers Notes on Field Assessment Form (Y/N) NO Presence of regulatory considerations (Y/N) YES Wetland is intensively managed (Y/N) Assessment area is located within 50 feet of a natural tributary or other open water (Y/N) Assessment area is substantially altered by beaver (Y/N) NO Assessment area experiences overbank flooding during normal rainfall conditions (Y/N) NO Assessment area is on a coastal island (Y/N) NO Sub -function Ratina Summa Function Sub -function Metrics Rating Hydrology Surface Storage and Retention Condition NA Sub -surface Storage and Retention Condition NA 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 LOW Vegetation Composition Condition LOW Function Ratina Summa Function Metrics Rating Hydrology Condition MEDIUM Water Quality Condition HIGH Condition/Opportunity HIGH Opportunity Presence (Y/N) NO Habitat Condition LOW Overall Wetland Rating MEDIUM NC WAM FIELD ASSESSMENT FORM Accompanies user manuai version am USACE AID # NCDWR# Project Name EB-6038 Date of Evaluation 1/27/20 Applicant/Owner Name City of Hickory, Jag Properties LLC, Wetland Site Name WC Summit Offices Wetland Type Basin Wetland Assessor Name/Organization Ran Elliott / TGS Engineers Level III Ecoregion Piedmont Nearest Named Water Body Catawba River River Basin Catawba USGS 8-Digit Catalogue Unit 03050101 County Catawba NCDWR Region Mooresville ® Yes ❑ No Precipitation within 48 hrs? Latitude/Longitude (deci-degrees) 35.748902,-81.371372 Evidence of stressors affecting the assessment area (may not be within the assessment area) Please circle and/or make note on the last page 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 Regulatory Considerations - Were regulatory considerations evaluated? ®Yes ❑No If Yes, check all that apply to the assessment area. ❑ Anadromous fish ❑ Federally protected species or State endangered or threatened species ® NCDWR 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 Does the assessment area experience overbank flooding during normal rainfall conditions? ❑ 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], hydrologic alteration) 2. 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. 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). 3. Water Storage/Surface Relief — assessment area/wetland type condition metric (skip for all marshes) Check a box in each column. Select the appropriate storage for the assessment area (AA) and the wetland type (WT). AA WT 3a. ❑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 3b. ❑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 (skip for all marshes) 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. 4a. ❑A Sandy soil ®B Loamy or clayey soils exhibiting redoximorphic features (concentrations, depletions, or rhizospheres) ❑C Loamy or clayey soils not exhibiting redoximorphic features ❑D Loamy or clayey gleyed soil ❑E Histosol or histic epipedon 4b. ®A Soil ribbon < 1 inch ❑B Soil ribbon >_ 1 inch 4c. ®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) 6. Land Use — opportunity metric (skip for non -riparian wetlands) Check all that apply (at least one box in each column). Evaluation involves a GIS effort with field adjustment. Consider sources draining to assessment area within entire upstream watershed (WS), within 5 miles and within the watershed draining to the assessment area (5M), and within 2 miles and within the watershed draining to the assessment area (2M). WS 5M 2M ❑A ❑A ❑A > 10% impervious surfaces ❑B ❑B ❑B Confined animal operations (or other local, concentrated source of pollutants ❑C ❑C ❑C >_ 20% coverage of pasture ❑D ❑D ❑D >_ 20% coverage of agricultural land (regularly plowed land) ❑E ❑E ❑E >_ 20% coverage of maintained grass/herb ❑F ❑F ❑F >_ 20% coverage of clear-cut land ❑G ❑G ❑G Little or no opportunity to improve water quality. Lack of opportunity may result from little or no disturbance in the watershed or hydrologic alterations that prevent drainage and/or overbank flow from affecting the assessment area. 7. Wetland Acting as Vegetated Buffer— assessment area/wetland complex condition metric (skip for non -riparian wetlands) 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? (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.) ❑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. 05 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. El 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 (evaluate WT for all marshes and Estuarine Woody Wetland only; evaluate WC for Bottomland Hardwood Forest, Headwater Forest, and Riverine Swamp Forest only) Check a box in each column for riverine wetlands only. Select the average 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 (skip for non -riparian wetlands) Answer for assessment area dominant landform. ❑A Evidence of short -duration inundation (< 7 consecutive days) ❑B Evidence of saturation, without evidence of inundation El 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 (skip for non -riparian wetlands and all marshes) 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 01 01 El 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, regularly maintained utility line corridors the width of a four -lane road or wider, 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 (skip for all marshes and Estuarine Woody Wetland) May involve a GIS effort with field adjustment. Estimate distance from wetland type boundary to artificial edges. Artificial edges include non -forested areas >_ 40 feet wide such as fields, development, roads, regularly maintained utility line corridors, and clear -cuts. Consider the eight main points of the compass. Artificial edge occurs within 150 feet in how many directions? If the assessment area is clear cut, select option "C." ❑A 0 ❑B 1 to 4 ®C 5to8 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, or expected species are unnaturally absent (planted stands of non - characteristic species or at least one stratum inappropriately composed of a single species), or exotic species are dominant in at least one stratum. 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 assessment area 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 o ❑A ❑A Canopy closed, or nearly closed, with natural gaps associated with natural processes ❑B ❑B Canopy present, but opened more than natural gaps U ®C ®C Canopy sparse or absent >, o ❑A ❑A Dense mid-story/sapling layer co ❑B ❑B Moderate density mid-story/sapling layer ®C ®C Mid-story/sapling layer sparse or absent ❑A ❑A Dense shrub layer .L ❑B ❑B Moderate density shrub layer U) ®C ®C Shrub layer sparse or absent M ❑A ❑A Dense herb layer _ ®B ®B Moderate density herb layer ❑C ❑C Herb layer sparse or absent 18. Snags — wetland type condition metric (skip for all marshes) ❑A Large snags (more than one) are visible (> 12 inches DBH, or large relative to species present and landscape stability). ®B Not A 19. Diameter Class Distribution — wetland type condition metric (skip for all marshes) ❑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 (skip for all marshes) 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 Not 21. Vegetation/Open Water Dispersion — wetland type/open water condition metric (evaluate for Non -Tidal Freshwater Marsh only) Select the figure that best describes the amount of interspersion between vegetation and open water in the growing season. Patterned areas indicate vegetated areas, while solid white areas indicate open water. ❑A ❑B ❑C ❑D N PP 1 ^ 22. Hydrologic Connectivity — assessment area condition metric (evaluate for riparian wetlands and Salt/Brackish Marsh 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. Documentation required if evaluated as B, C, or D. ❑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 The wetland area is located in a frequently maintained field. NC WAM Wetland Rating Sheet Accompanies User Manual Version 5.0 Wetland Site Name WC Date of Assessment 1/27/20 Wetland Type Basin Wetland Ryan Elliott / TGS Assessor Name/Organization Engineers Notes on Field Assessment Form (Y/N) YES Presence of regulatory considerations (Y/N) YES Wetland is intensively managed (Y/N) YES Assessment area is located within 50 feet of a natural tributary or other open water (Y/N) Assessment area is substantially altered by beaver (Y/N) NO Assessment area experiences overbank flooding during normal rainfall conditions (Y/N) NO Assessment area is on a coastal island (Y/N) NO Sub -function Ratina Summa Function Sub -function Metrics Rating Hydrology Surface Storage and Retention Condition NA Sub -surface Storage and Retention Condition NA 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 MEDIUM Condition/Opportunity MEDIUM Opportunity Presence (Y/N) NO Habitat Physical Structure Condition LOW Landscape Patch Structure Condition LOW Vegetation Composition Condition LOW Function Ratina Summa Function Metrics Rating Hydrology Condition MEDIUM Water Quality Condition MEDIUM Condition/Opportunity MEDIUM Opportunity Presence (Y/N) NO Habitat Condition LOW Overall Wetland Rating MEDIUM NC WAM FIELD ASSESSMENT FORM Accompanies user manuai version am USACE AID # NCDWR# Project Name EB-6038 Date of Evaluation 1/27/20 Applicant/Owner Name City of Hickory, City of Hickory Wetland Site Name WD Wetland Type Headwater Forest Assessor Name/Organization Ran Elliott / TGS Engineers Level III Ecoregion Piedmont Nearest Named Water Body Catawba River River Basin Catawba USGS 8-Digit Catalogue Unit 03050101 County Burke NCDWR Region Mooresville ® Yes ❑ No Precipitation within 48 hrs? Latitude/Longitude (deci-degrees) 35.744113,-81.386448 Evidence of stressors affecting the assessment area (may not be within the assessment area) Please circle and/or make note on the last page 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 Regulatory Considerations -Were regulatory considerations evaluated? ®Yes ❑No If Yes, check all that apply to the assessment area. ❑ Anadromous fish ❑ Federally protected species or State endangered or threatened species ® NCDWR 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 Does the assessment area experience overbank flooding during normal rainfall conditions? ❑ 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], hydrologic alteration) 2. 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. 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). 3. Water Storage/Surface Relief —assessment area/wetland type condition metric (skip for all marshes) Check a box in each column. Select the appropriate storage for the assessment area (AA) and the wetland type (WT). AA WT 3a. ❑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 3b. ❑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 (skip for all marshes) 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. 4a. ❑A Sandy soil ❑B Loamy or clayey soils exhibiting redoximorphic features (concentrations, depletions, or rhizospheres) ®C Loamy or clayey soils not exhibiting redoximorphic features ❑D Loamy or clayey gleyed soil ❑E Histosol or histic epipedon 4b. ®A Soil ribbon < 1 inch ❑B Soil ribbon >_ 1 inch 4c. ®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) 6. Land Use — opportunity metric (skip for non -riparian wetlands) Check all that apply (at least one box in each column). Evaluation involves a GIS effort with field adjustment. Consider sources draining to assessment area within entire upstream watershed (WS), within 5 miles and within the watershed draining to the assessment area (5M), and within 2 miles and within the watershed draining to the assessment area (2M). WS 5M 2M ®A ®A ®A > 10% impervious surfaces ❑B ❑B ❑B Confined animal operations (or other local, concentrated source of pollutants ❑C ❑C ❑C >_ 20% coverage of pasture ❑D ❑D ❑D >_ 20% coverage of agricultural land (regularly plowed land) ®E ®E ®E >_ 20% coverage of maintained grass/herb ❑F ❑F ❑F >_ 20% coverage of clear-cut land ❑G ❑G ❑G Little or no opportunity to improve water quality. Lack of opportunity may result from little or no disturbance in the watershed or hydrologic alterations that prevent drainage and/or overbank flow from affecting the assessment area. 7. Wetland Acting as Vegetated Buffer— assessment area/wetland complex condition metric (skip for non -riparian wetlands) 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? (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.) ❑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. 05 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. El 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 (evaluate WT for all marshes and Estuarine Woody Wetland only; evaluate WC for Bottomland Hardwood Forest, Headwater Forest, and Riverine Swamp Forest only) Check a box in each column for riverine wetlands only. Select the average 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 (skip for non -riparian wetlands) Answer for assessment area dominant landform. ®A Evidence of short -duration inundation (< 7 consecutive days) ❑B Evidence of saturation, without evidence of inundation El 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 (skip for non -riparian wetlands and all marshes) 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 El El El 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, regularly maintained utility line corridors the width of a four -lane road or wider, 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 (skip for all marshes and Estuarine Woody Wetland) May involve a GIS effort with field adjustment. Estimate distance from wetland type boundary to artificial edges. Artificial edges include non -forested areas >_ 40 feet wide such as fields, development, roads, regularly maintained utility line corridors, and clear -cuts. Consider the eight main points of the compass. Artificial edge occurs within 150 feet in how many directions? If the assessment area is clear cut, select option "C." ❑A 0 ®B 1 to 4 ❑C 5to8 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, or expected species are unnaturally absent (planted stands of non - characteristic species or at least one stratum inappropriately composed of a single species), or exotic species are dominant in at least one stratum. 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 assessment area 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 o ®A ®A Canopy closed, or nearly closed, with natural gaps associated with natural processes ❑B ❑B Canopy present, but opened more than natural gaps U ❑C ❑C Canopy sparse or absent >, o ❑A ❑A Dense mid-story/sapling layer co ®B ®B Moderate density mid-story/sapling layer ❑C ❑C Mid-story/sapling layer sparse or absent ❑A ❑A Dense shrub layer .L ®B ®B Moderate density shrub layer u) ❑C ❑C Shrub layer sparse or absent -0 ❑A ❑A Dense herb layer _ ❑B ❑B Moderate density herb layer ®C ®C Herb layer sparse or absent 18. Snags — wetland type condition metric (skip for all marshes) ❑A Large snags (more than one) are visible (> 12 inches DBH, or large relative to species present and landscape stability). ®B Not A 19. Diameter Class Distribution — wetland type condition metric (skip for all marshes) ®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 (skip for all marshes) 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 Not 21. Vegetation/Open Water Dispersion — wetland type/open water condition metric (evaluate for Non -Tidal Freshwater Marsh only) Select the figure that best describes the amount of interspersion between vegetation and open water in the growing season. Patterned areas indicate vegetated areas, while solid white areas indicate open water. ❑A ❑B ❑C ❑D N PP 1 ^ 22. Hydrologic Connectivity — assessment area condition metric (evaluate for riparian wetlands and Salt/Brackish Marsh 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. Documentation required if evaluated as B, C, or D. ®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 Adjacent to drainage pipe. Water channelizes after wetland complex outside project study area. NC WAM Wetland Rating Sheet Accompanies User Manual Version 5.0 Wetland Site Name WD Date of Assessment 1/27/20 Wetland Type Headwater Forest Ryan Elliott / TGS Assessor Name/Organization Engineers 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 Assessment area experiences overbank flooding during normal rainfall conditions (Y/N) NO Assessment area is on a coastal island (Y/N) NO Sub -function Ratina Summa Function Sub -function Metrics Rating Hydrology Surface Storage and Retention Condition HIGH Sub -surface Storage and Retention Condition HIGH Water Quality Pathogen Change Condition HIGH Condition/Opportunity HIGH Opportunity Presence (Y/N) YES Particulate Change Condition HIGH Condition/Opportunity NA Opportunity Presence (Y/N) NA Soluble Change Condition MEDIUM Condition/Opportunity HIGH Opportunity Presence (Y/N) YES Physical Change Condition LOW Condition/Opportunity LOW Opportunity Presence (Y/N) YES Pollution Change Condition NA Condition/Opportunity NA Opportunity Presence (Y/N) NA Habitat Physical Structure Condition HIGH Landscape Patch Structure Condition LOW Vegetation Composition Condition LOW Function Ratina Summa Function Metrics Rating Hydrology Condition HIGH Water Quality Condition HIGH Condition/Opportunity HIGH Opportunity Presence (Y/N) YES Habitat Condition LOW Overall Wetland Rating HIGH NC WAM FIELD ASSESSMENT FORM Accompanies user manuai version am USACE AID # NCDWR# Project Name EB-6038 Date of Evaluation 1/27/20 Applicant/Owner Name City of Hickory, City of Hickory Wetland Site Name WE Wetland Type Headwater Forest Assessor Name/Organization Ran Elliott / TGS Engineers Level III Ecoregion Piedmont Nearest Named Water Body Catawba River River Basin Catawba USGS 8-Digit Catalogue Unit 03050101 County Burke NCDWR Region Mooresville ® Yes ❑ No Precipitation within 48 hrs? Latitude/Longitude (deci-degrees) 35.744136,-81.386558 Evidence of stressors affecting the assessment area (may not be within the assessment area) Please circle and/or make note on the last page 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 Regulatory Considerations -Were regulatory considerations evaluated? ®Yes ❑No If Yes, check all that apply to the assessment area. ❑ Anadromous fish ❑ Federally protected species or State endangered or threatened species ® NCDWR 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 Does the assessment area experience overbank flooding during normal rainfall conditions? ❑ 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], hydrologic alteration) 2. 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. 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). 3. Water Storage/Surface Relief —assessment area/wetland type condition metric (skip for all marshes) Check a box in each column. Select the appropriate storage for the assessment area (AA) and the wetland type (WT). AA WT 3a. ❑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 3b. ❑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 (skip for all marshes) 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. 4a. ❑A Sandy soil ®B Loamy or clayey soils exhibiting redoximorphic features (concentrations, depletions, or rhizospheres) ❑C Loamy or clayey soils not exhibiting redoximorphic features ❑D Loamy or clayey gleyed soil ❑E Histosol or histic epipedon 4b. ®A Soil ribbon < 1 inch ❑B Soil ribbon >_ 1 inch 4c. ®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) 6. Land Use — opportunity metric (skip for non -riparian wetlands) Check all that apply (at least one box in each column). Evaluation involves a GIS effort with field adjustment. Consider sources draining to assessment area within entire upstream watershed (WS), within 5 miles and within the watershed draining to the assessment area (5M), and within 2 miles and within the watershed draining to the assessment area (2M). WS 5M 2M ®A ®A ®A > 10% impervious surfaces ❑B ❑B ❑B Confined animal operations (or other local, concentrated source of pollutants ❑C ❑C ❑C >_ 20% coverage of pasture ❑D ❑D ❑D >_ 20% coverage of agricultural land (regularly plowed land) ®E ®E ®E >_ 20% coverage of maintained grass/herb ❑F ❑F ❑F >_ 20% coverage of clear-cut land ❑G ❑G ❑G Little or no opportunity to improve water quality. Lack of opportunity may result from little or no disturbance in the watershed or hydrologic alterations that prevent drainage and/or overbank flow from affecting the assessment area. 7. Wetland Acting as Vegetated Buffer— assessment area/wetland complex condition metric (skip for non -riparian wetlands) 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? (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.) ❑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. 05 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. El 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 (evaluate WT for all marshes and Estuarine Woody Wetland only; evaluate WC for Bottomland Hardwood Forest, Headwater Forest, and Riverine Swamp Forest only) Check a box in each column for riverine wetlands only. Select the average 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 (skip for non -riparian wetlands) 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 (skip for non -riparian wetlands and all marshes) 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 El El El 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, regularly maintained utility line corridors the width of a four -lane road or wider, 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 (skip for all marshes and Estuarine Woody Wetland) May involve a GIS effort with field adjustment. Estimate distance from wetland type boundary to artificial edges. Artificial edges include non -forested areas >_ 40 feet wide such as fields, development, roads, regularly maintained utility line corridors, and clear -cuts. Consider the eight main points of the compass. Artificial edge occurs within 150 feet in how many directions? If the assessment area is clear cut, select option "C." ❑A 0 ®B 1 to 4 ❑C 5to8 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, or expected species are unnaturally absent (planted stands of non - characteristic species or at least one stratum inappropriately composed of a single species), or exotic species are dominant in at least one stratum. 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 assessment area 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 o ®A ®A Canopy closed, or nearly closed, with natural gaps associated with natural processes ❑B ❑B Canopy present, but opened more than natural gaps U ❑C ❑C Canopy sparse or absent >, o ❑A ❑A Dense mid-story/sapling layer co ®B ®B Moderate density mid-story/sapling layer ❑C ❑C Mid-story/sapling layer sparse or absent ❑A ❑A Dense shrub layer .L ®B ®B Moderate density shrub layer u) ❑C ❑C Shrub layer sparse or absent -0 ❑A ❑A Dense herb layer _ ❑B ❑B Moderate density herb layer ®C ®C Herb layer sparse or absent 18. Snags — wetland type condition metric (skip for all marshes) ❑A Large snags (more than one) are visible (> 12 inches DBH, or large relative to species present and landscape stability). ®B Not A 19. Diameter Class Distribution — wetland type condition metric (skip for all marshes) ®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 (skip for all marshes) 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 Not 21. Vegetation/Open Water Dispersion — wetland type/open water condition metric (evaluate for Non -Tidal Freshwater Marsh only) Select the figure that best describes the amount of interspersion between vegetation and open water in the growing season. Patterned areas indicate vegetated areas, while solid white areas indicate open water. ❑A ❑B ❑C ❑D N PP 1 ^ 22. Hydrologic Connectivity — assessment area condition metric (evaluate for riparian wetlands and Salt/Brackish Marsh 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. Documentation required if evaluated as B, C, or D. ®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 Adjacent to drainage pipe. Water channelizes after wetland complex outside project study area. NC WAM Wetland Rating Sheet Accompanies User Manual Version 5.0 Wetland Site Name WE Date of Assessment 1/27/20 Wetland Type Headwater Forest Ryan Elliott / TGS Assessor Name/Organization Engineers 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 Assessment area experiences overbank flooding during normal rainfall conditions (Y/N) NO Assessment area is on a coastal island (Y/N) NO Sub -function Ratina Summa Function Sub -function Metrics Rating Hydrology Surface Storage and Retention Condition HIGH Sub -surface Storage and Retention Condition HIGH Water Quality Pathogen Change Condition HIGH Condition/Opportunity HIGH Opportunity Presence (Y/N) YES Particulate Change Condition HIGH Condition/Opportunity NA Opportunity Presence (Y/N) NA Soluble Change Condition MEDIUM Condition/Opportunity HIGH Opportunity Presence (Y/N) YES Physical Change Condition MEDIUM Condition/Opportunity HIGH Opportunity Presence (Y/N) YES Pollution Change Condition NA Condition/Opportunity NA Opportunity Presence (Y/N) NA Habitat Physical Structure Condition HIGH Landscape Patch Structure Condition LOW Vegetation Composition Condition LOW Function Ratina Summa Function Metrics Rating Hydrology Condition HIGH Water Quality Condition HIGH Condition/Opportunity HIGH Opportunity Presence (Y/N) YES Habitat Condition LOW Overall Wetland Rating HIGH NC WAM FIELD ASSESSMENT FORM Accompanies user manuai version am USACE AID # NCDWR# Project Name EB-6038 Date of Evaluation 2/25/20 Applicant/Owner Name City of Hickory, City of Hickory Wetland Site Name WF Wetland Type Non -Tidal Freshwater Marsh Assessor Name/Organization Ran Elliott / TGS Engineers Level III Ecoregion Piedmont Nearest Named Water Body Catawba River River Basin Catawba USGS 8-Digit Catalogue Unit 03050101 County Burke NCDWR Region Mooresville ® Yes ❑ No Precipitation within 48 hrs? Latitude/Longitude (deci-degrees) 35.745545,-81.381395 Evidence of stressors affecting the assessment area (may not be within the assessment area) Please circle and/or make note on the last page 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 Regulatory Considerations -Were regulatory considerations evaluated? ®Yes ❑No If Yes, check all that apply to the assessment area. ❑ Anadromous fish ❑ Federally protected species or State endangered or threatened species ® NCDWR 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 Does the assessment area experience overbank flooding during normal rainfall conditions? ❑ 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], hydrologic alteration) 2. 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. 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). 3. Water Storage/Surface Relief —assessment area/wetland type condition metric (skip for all marshes) Check a box in each column. Select the appropriate storage for the assessment area (AA) and the wetland type (WT). AA WT 3a. ❑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 3b. ❑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 (skip for all marshes) 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. 4a. ❑A Sandy soil ❑B Loamy or clayey soils exhibiting redoximorphic features (concentrations, depletions, or rhizospheres) ❑C Loamy or clayey soils not exhibiting redoximorphic features ❑D Loamy or clayey gleyed soil ❑E Histosol or histic epipedon 4b. ❑A Soil ribbon < 1 inch ❑B Soil ribbon >_ 1 inch 4c. ❑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) 6. Land Use — opportunity metric (skip for non -riparian wetlands) Check all that apply (at least one box in each column). Evaluation involves a GIS effort with field adjustment. Consider sources draining to assessment area within entire upstream watershed (WS), within 5 miles and within the watershed draining to the assessment area (5M), and within 2 miles and within the watershed draining to the assessment area (2M). WS 5M 2M ®A ®A ®A > 10% impervious surfaces ❑B ❑B ❑B Confined animal operations (or other local, concentrated source of pollutants ❑C ❑C ❑C >_ 20% coverage of pasture ❑D ❑D ❑D >_ 20% coverage of agricultural land (regularly plowed land) ®E ®E ®E >_ 20% coverage of maintained grass/herb ❑F ❑F ❑F >_ 20% coverage of clear-cut land ❑G ❑G ❑G Little or no opportunity to improve water quality. Lack of opportunity may result from little or no disturbance in the watershed or hydrologic alterations that prevent drainage and/or overbank flow from affecting the assessment area. 7. Wetland Acting as Vegetated Buffer— assessment area/wetland complex condition metric (skip for non -riparian wetlands) 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? (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.) ❑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. 05 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. El 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 (evaluate WT for all marshes and Estuarine Woody Wetland only; evaluate WC for Bottomland Hardwood Forest, Headwater Forest, and Riverine Swamp Forest only) Check a box in each column for riverine wetlands only. Select the average 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 (skip for non -riparian wetlands) Answer for assessment area dominant landform. ®A Evidence of short -duration inundation (< 7 consecutive days) ❑B Evidence of saturation, without evidence of inundation El 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 (skip for non -riparian wetlands and all marshes) 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 El El El 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, regularly maintained utility line corridors the width of a four -lane road or wider, 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 (skip for all marshes and Estuarine Woody Wetland) May involve a GIS effort with field adjustment. Estimate distance from wetland type boundary to artificial edges. Artificial edges include non -forested areas >_ 40 feet wide such as fields, development, roads, regularly maintained utility line corridors, and clear -cuts. Consider the eight main points of the compass. Artificial edge occurs within 150 feet in how many directions? If the assessment area is clear cut, select option "C." ❑A 0 ❑B 1 to 4 ❑C 5to8 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, or expected species are unnaturally absent (planted stands of non - characteristic species or at least one stratum inappropriately composed of a single species), or exotic species are dominant in at least one stratum. 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 assessment area 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 o ❑A ❑A Canopy closed, or nearly closed, with natural gaps associated with natural processes ❑B ❑B Canopy present, but opened more than natural gaps U ❑C ❑C Canopy sparse or absent >, o ❑A ❑A Dense mid-story/sapling layer co ❑B ❑B Moderate density mid-story/sapling layer ❑C ❑C Mid-story/sapling layer sparse or absent ❑A ❑A Dense shrub layer .L ❑B ❑B Moderate density shrub layer U) ❑C ❑C Shrub layer sparse or absent M ❑A ❑A Dense herb layer _ ❑B ❑B Moderate density herb layer ❑C ❑C Herb layer sparse or absent 18. Snags — wetland type condition metric (skip for all marshes) ❑A Large snags (more than one) are visible (> 12 inches DBH, or large relative to species present and landscape stability). ❑B Not A 19. Diameter Class Distribution — wetland type condition metric (skip for all marshes) ❑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 (skip for all marshes) 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 Not 21. Vegetation/Open Water Dispersion — wetland type/open water condition metric (evaluate for Non -Tidal Freshwater Marsh only) Select the figure that best describes the amount of interspersion between vegetation and open water in the growing season. Patterned areas indicate vegetated areas, while solid white areas indicate open water. ❑A ®B ❑C ❑D � � y l l A 22. Hydrologic Connectivity — assessment area condition metric (evaluate for riparian wetlands and Salt/Brackish Marsh 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. Documentation required if evaluated as B, C, or D. ®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 Adjacent to drainage pipe. Water channelizes after wetland complex outside project study area. NC WAM Wetland Rating Sheet Accompanies User Manual Version 5.0 Wetland Site Name WF Date of Assessment 2/25/20 Wetland Type Non -Tidal Freshwater Marsh Ryan Elliott / TGS Assessor Name/Organization Engineers 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 Assessment area experiences overbank flooding during normal rainfall conditions (Y/N) NO Assessment area is on a coastal island (Y/N) NO Sub -function Ratina Summa Function Sub -function Metrics Rating Hydrology Surface Storage and Retention Condition NA Sub -surface Storage and Retention Condition NA 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 NA Condition/Opportunity NA Opportunity Presence (Y/N) NA Habitat Physical Structure Condition HIGH Landscape Patch Structure Condition LOW Vegetation Composition Condition MEDIUM Function Ratina Summa Function Metrics Rating Hydrology Condition HIGH Water Quality Condition MEDIUM Condition/Opportunity HIGH Opportunity Presence (Y/N) YES Habitat Condition MEDIUM Overall Wetland Rating MEDIUM Stream ID: SB NC DWQ Stream Identification Form Version 4.11 Date: 1/14/2020 Project/Site: EB-6038 Latitude: 35.749303 Evaluator: Ryan Elliott County: Catawba -81.377204 Longitude: Total Points: other: Longview Stream is at least intermittent if 17 Stream Ephemeral e. . Quad Name: 9 > 19 or perennial if 30 - P Determination: A. Geomorphology Subtotal = 11 Absent Weak Moderate Strong SCORE 1a. Continuous bed and bank 0 1 2 3 2 2. Sinuosity of channel along thalweg 0 1 2 3 2 3. In -Channel structure: ex. riffle -pool, step -pool, ripple- pool sequence 0 1 2 3 1 4. Particle size of stream substrate 0 1 2 3 1 5. Active/relic floodplain 0 1 2 3 1 6. Depositional bars or benches 0 1 2 3 1 7. Recent alluvial deposits 0 1 2 3 2 8. Headcuts 0 1 2 3 0 9. Grade controls 0 0.5 1 1.5 0.5 10. Natural valley 0 0.5 1 1.5 0.5 11. Second or greater order channel No = 0 Yes = 3 0 artificial ditches are not rated; see discussions in manual. B. Hydrology Subtotal = 3.5 Absent Weak Moderate Strong SCORE 12. Presence of Baseflow 0 1 2 3 1 13. Iron oxidizing bacteria 0 1 2 3 0 14. Leaflitter 1.5 1 0.5 0 0.5 15. Sediment on plants or debris 0 1 0.5 1 1 1.5 1 16. Organic debris lines or piles 0 1 0.5 1 1 1.5 1 17. Soil -based evidence of high water table? No = 0 Yes = 3 0 C. Biology Subtotal = 2.5 Absent Weak Moderate Strong SCORE 18. Fibrous roots in streambed 3 2 1 0 0 19. Rooted upland plants in streambed 3 2 1 0 2 20. Macrobenthos (note diversity and abundance) 0 1 2 3 0 21. Aquatic Mollusks 0 1 2 3 0 22. Fish 0 0.5 1 1.5 0 23. Crayfish 0 0.5 1 1.5 0 24. Amphibians 0 0.5 1 1.5 0 25. Algae 0 0.5 1 1.5 0.5 26. Wetland plants in streambed FACW=0.75; OBL=1.5 Other=0 0 'perennial stream may also be identified using other methods. See p.35 of manual. Notes: Evaluation was after a rain event Bank Height (feet) 0-1' Bankfull Width (feet) 1-3' Water Depth (inches) 1-4" Channel Substrate Sand, gravel Velocity: Slow Clarity: Clear Sketch: Stream ID: SC NC DWQ Stream Identification Form Version 4.11 Date: 1/14/2020 Project/Site: EB-6038 Latitude: 35.749196 Evaluator: Ryan Elliott County: Catawba -81.377212 Longitude: Total Points: other: Longview Stream is at least intermittent if 24 Stream Intermittent e. . Quad Name: 9 > 19 or perennial if 30 - P Determination: A. Geomorphology Subtotal = 14 Absent Weak Moderate Strong SCORE 1a. Continuous bed and bank 0 1 2 3 2 2. Sinuosity of channel along thalweg 0 1 2 3 2 3. In -Channel structure: ex. riffle -pool, step -pool, ripple- pool sequence 0 1 2 3 2 4. Particle size of stream substrate 0 1 2 3 2 5. Active/relic floodplain 0 1 2 3 1 6. Depositional bars or benches 0 1 2 3 1 7. Recent alluvial deposits 0 1 2 3 2 8. Headcuts 0 1 2 3 0.5 9. Grade controls 0 0.5 1 1.5 0.5 10. Natural valley 0 0.5 1 1.5 1 11. Second or greater order channel No = 0 Yes = 3 0 artificial ditches are not rated; see discussions in manual. B. Hydrology Subtotal = 5 Absent Weak Moderate Strong SCORE 12. Presence of Baseflow 0 1 2 3 2 13. Iron oxidizing bacteria 0 1 2 3 0 14. Leaflitter 1.5 1 0.5 0 1 15. Sediment on plants or debris 0 1 0.5 1 1 1.5 1 16. Organic debris lines or piles 0 1 0.5 1 1 1.5 1 17. Soil -based evidence of high water table? No = 0 Yes = 3 0 C. Biology Subtotal = 5 Absent Weak Moderate Strong SCORE 18. Fibrous roots in streambed 3 2 1 0 1 19. Rooted upland plants in streambed 3 2 1 0 3 20. Macrobenthos (note diversity and abundance) 0 1 2 3 0 21. Aquatic Mollusks 0 1 2 3 0 22. Fish 0 0.5 1 1.5 0 23. Crayfish 0 0.5 1 1.5 0 24. Amphibians 0 0.5 1 1.5 0 25. Algae 0 0.5 1 1.5 1 26. Wetland plants in streambed FACW=0.75; OBL=1.5 Other=0 0 'perennial stream may also be identified using other methods. See p.35 of manual. Notes: Evaluation was after a rain event Bank Height (feet) 0-1' Bankfull Width (feet) 1-3' Water Depth (inches) 1-3" Channel Substrate Sand, gravel, cobble Velocity: Moderate Clarity: Clear Sketch: Stream ID: SD NC DWQ Stream Identification Form Version 4.11 Date: 1/25/2020 Project/Site: EB-6038 Latitude: 35.744779 Evaluator: Ryan Elliott County: Catawba -81.361428 Longitude: Total Points: other: Longview Stream is at least intermittent if 26.5 Stream Intermittent e. . Quad Name: 9 > 19 or perennial if 30 - P Determination: A. Geomorphology Subtotal = 11.5 Absent Weak Moderate Strong SCORE 1a. Continuous bed and bank 0 1 2 3 3 2. Sinuosity of channel along thalweg 0 1 2 3 0 3. In -Channel structure: ex. riffle -pool, step -pool, ripple- pool sequence 0 1 2 3 2 4. Particle size of stream substrate 0 1 2 3 2 5. Active/relic floodplain 0 1 2 3 0 6. Depositional bars or benches 0 1 2 3 2 7. Recent alluvial deposits 0 1 2 3 2 8. Headcuts 0 1 2 3 0 9. Grade controls 0 0.5 1 1.5 0 10. Natural valley 0 0.5 1 1.5 0.5 11. Second or greater order channel No = 0 Yes = 3 0 artificial ditches are not rated; see discussions in manual. B. Hydrology Subtotal = 8 Absent Weak Moderate Strong SCORE 12. Presence of Baseflow 0 1 2 3 2 13. Iron oxidizing bacteria 0 1 2 3 0 14. Leaflitter 1.5 1 0.5 0 1.5 15. Sediment on plants or debris 0 1 0.5 1 1 1.5 1 16. Organic debris lines or piles 0 1 0.5 1 1 1.5 0.5 17. Soil -based evidence of high water table? No = 0 Yes = 3 3 C. Biology Subtotal = 7 Absent Weak Moderate Strong SCORE 18. Fibrous roots in streambed 3 2 1 0 3 19. Rooted upland plants in streambed 3 2 1 0 3 20. Macrobenthos (note diversity and abundance) 0 1 2 3 0 21. Aquatic Mollusks 0 1 2 3 0 22. Fish 0 0.5 1 1.5 0 23. Crayfish 0 0.5 1 1.5 0 24. Amphibians 0 0.5 1 1.5 0 25. Algae 0 0.5 1 1.5 1 26. Wetland plants in streambed FACW=0.75; OBL=1.5 Other=0 0 'perennial stream may also be identified using other methods. See p.35 of manual. Notes: Evaluation was after a rain event Bank Height (feet) 1-2' Bankfull Width (feet) 1-3' Water Depth (inches) 3-6" Channel Substrate Sand, gravel, cobble, boulder Velocity: Moderate Clarity: Slightly turbid Sketch: PRELIMINARY JURISDICTIONAL DETERMINATION (PJD) FORM BACKGROUND INFORMATION A. REPORT COMPLETION DATE FOR PJD: 3/12/2020 B. NAME AND ADDRESS OF PERSON REQUESTING PJD: TGS Engineers Attn: Ryan Elliott 706 Hillsborough St., Suite 200 Raleigh, NC 27603 C. DISTRICT OFFICE, FILE NAME, AND NUMBER: Charlotte Regulatory Field Office D. PROJECT LOCATION(S) AND BACKGROUND INFORMATION:). The proposed greenway project is located in the Town of Hickory in Catawba County, NC E. (USE THE TABLE BELOW TO DOCUMENT MULTIPLE AQUATIC RESOURCES AND/OR AQUATIC RESOURCES AT DIFFERENT SITES) State: North Carolina County/parish/borough: Catawba County City: Hickory Center coordinates of site (lat/long in degree decimal format): Lat.: 35.744891°N, 81.372268°W Universal Transverse Mercator: Zone 17S 466340 3955717 Name of nearest waterbody: Catawba River F. REVIEW PERFORMED FOR SITE EVALUATION (CHECK ALL THAT APPLY): ❑ Office (Desk) Determination. Date: ❑ Field Determination. Date(s): TABLE OF AQUATIC RESOURCES INREVIEW AREA WHICH "MAY BE" SUBJECT TO REGULATORY JURISDICTION. Site Number Latitude (decimal degrees) Longitude (decimal degrees) Estimated amount of aquatic resources in review area (acreage and linear feet, if applicable Type of aquatic resources (i.e., wetland vs. non- wetland waters Geographic authority to which the aquatic resource "may be" subject (i.e., Section 404 or Section 10/404) WA 35.7494180 N 81.3730160 W +/- 0.82 ac. Wetland Section 404 We 35.7490090 N 81.3711820 W +/- 0.16 ac. Wetland Section 404 WD 35.7441340 N 81.3864490 W +/- 0.01 ac. Wetland Section 404 WE 35.7441720 N 81.3866460 W +/- 0.03 ac. Wetland Section 404 WF 35.7455450 N 81.3813950 W +/- 0.09 ac. Wetland Section 404 SA 35.7470590 N 81.3814570 W +/- 918 LF Non -Wetland Section 404 SB 35.7493030 N 81.3772040 W +/- 21 LF Non -Wetland Section 404 Sc 35.7491960 N 81.3772120 W +/- 60 LF Non -Wetland Section 404 SD 35.7447790 N 81.3614280 W +/- 174 LF Non -Wetland Section 404 1) The Corps of Engineers believes that there may be jurisdictional aquatic resources in the review area, and the requestor of this PJD is hereby advised of his or her option to request and obtain an approved JD (AJD) for that review area based on an informed decision after having discussed the various types of JDs and their characteristics and circumstances when they may be appropriate. 2) In any circumstance where a permit applicant obtains an individual permit, or a Nationwide General Permit (NWP) or other general permit verification requiring "pre- construction notification" (PCN), or requests verification for a non -reporting NWP or other general permit, and the permit applicant has not requested an AJD for the activity, the permit applicant is hereby made aware that: (1) the permit applicant has elected to seek a permit authorization based on a PJD, which does not make an official determination of jurisdictional aquatic resources; (2) the applicant has the option to request an AJD before accepting the terms and conditions of the permit authorization, and that basing a permit authorization on an AJD could possibly result in less compensatory mitigation being required or different special conditions; (3) the applicant has the right to request an individual permit rather than accepting the terms and conditions of the NWP or other general permit authorization; (4) the applicant can accept a permit authorization and thereby agree to comply with all the terms and conditions of that permit, including whatever mitigation requirements the Corps has determined to be necessary; (5) undertaking any activity in reliance upon the subject permit authorization without requesting an AJD constitutes the applicant's acceptance of the use of the PJD; (6) accepting a permit authorization (e.g., signing a proffered individual permit) or undertaking any activity in reliance on any form of Corps permit authorization based on a PJD constitutes agreement that all aquatic resources in the review area affected in any way by that activity will be treated as jurisdictional, and waives any challenge to such jurisdiction in any administrative or judicial compliance or enforcement action, or in any administrative appeal or in any Federal court; and (7) whether the applicant elects to use either an AJD or a PJD, the JD will be processed as soon as practicable. Further, an AJD, a proffered individual permit (and all terms and conditions contained therein), or individual permit denial can be administratively appealed pursuant to 33 C.F.R. Part 331. If, during an administrative appeal, it becomes appropriate to make an official determination whether geographic jurisdiction exists over aquatic resources in the review area, or to provide an official delineation of jurisdictional aquatic resources in the review area, the Corps will provide an AJD to accomplish that result, as soon as is practicable. This PJD finds that there "may be" waters of the U.S. and/or that there "may be navigable waters of the U.S. on the subject review area, and identifies all aquatic features in the review area that could be affected by the proposed activity, based on the following information: SUPPORTING DATA. Data reviewed for PJD (check all that apply) Checked items should be included in subject file. Appropriately reference sources below where indicated for all checked items: ® Maps, plans, plots or plat submitted by or on behalf of the PJD requestor: Map: Figure 3- Stream and Wetland Sketch Map ® Data sheets prepared/submitted by or on behalf of the PJD requestor. ❑ Office concurs with data sheets/delineation report. ❑ Office does not concur with data sheets/delineation report. Rationale: ❑ Data sheets prepared by the Corps: ❑ Corps navigable waters' study: ❑ U.S. Geological Survey Hydrologic Atlas: ❑ USGS NHD data. ❑ USGS 8 and 12 digit HUC maps. ® U.S. Geological Survey map(s). Cite scale & quad name: 1:24,000 Granite Falls, Bethlehem, Longview, and Hickory NC Quadrangles ❑ Natural Resources Conservation Service Soil Survey. ❑ National wetlands inventory map(s). Cite name: ❑ State/local wetland inventory map(s): ❑ FEMA/FIRM maps: ❑ 100-year Floodplain Elevation is: ❑ Photographs: ❑Aerial (Name & Date): or ❑Other (Name & Date): (National Geodetic Vertical Datum of 1929) ❑ Previous determination(s). File no. and date of response letter: ❑ Other information (please specify): IMPORTANT NOTE: The information recorded on this form has not necessarily been verified by the Corps and should not be relied upon for later jurisdictional detprminntianc_ Signature and date of Regulatory staff member completing PJD March 12, 2020 Signature and date of person requesting PJD (REQUIRED, unless obtaining the signature is impracticable) t 1 Districts may establish timeframes for requester to return signed PJD forms. If the requester does not respond within the established time frame, the district may presume concurrence and no additional follow up is necessary prior to finalizing an action. urisdictional Determination Reauest US Army Corps of Engineers WiGm+nglon District This form is intended for use by anyone requesting a jurisdictional determination (JD) from the U.S. Army Corps of Engineers, Wilmington District (Corps). Please include all supporting information, as described within each category, with your request. You may submit your request via mail, electronic mail, or facsimile. Requests should be sent to the appropriate project manager of the county in which the property is located. A current list of project managers by assigned counties can be found on-line at: http://www.saw.usace.gM.mil/Missions/Re ug latoI3 PermitProgram/Contact/CountyLocator.aspx, by calling 910-251-4633, or by contacting any of the field offices listed below. Once your request is received you will be contacted by a Corps project manager. ASHEVILLE & CHARLOTTE REGULATORY FIELD OFFICES US Army Corps of Engineers 151 Patton Avenue, Room 208 Asheville, North Carolina 28801-5006 General Number: (828) 271-7980 Fax Number: (828) 281-8120 RALEIGH REGULATORY FIELD OFFICE US Army Corps of Engineers 3331 Heritage Trade Drive, Suite 105 Wake Forest, North Carolina 27587 General Number: (919) 554-4884 Fax Number: (919) 562-0421 INSTRUCTIONS: WASHINGTON REGULATORY FIELD OFFICE US Army Corps of Engineers 2407 West Fifth Street Washington, North Carolina 27889 General Number: (910) 25 1-46 10 Fax Number: (252) 975-1399 WILMINGTON REGULATORY FIELD OFFICE US Army Corps of Engineers 69 Darlington Avenue Wilmington, North Carolina 28403 General Number: 910-251-4633 Fax Number: (910) 251-4025 All requestors must complete Parts A, B, C, D, E, F and G. NOTE TO CONSULTANTS AND AGENCIES: If you are requesting a JD on behalf of a paying client or your agency, please note the specific submittal requirements in Part H. NOTE ON PART D PROPERTY OWNER AUTHORIZATION: Please be aware that all JD requests must include the current property owner authorization for the Corps to proceed with the determination, which may include inspection of the property when necessary. This form must be signed by the current property owner(s) or the owner(s) authorized agent to be considered a complete request. NOTE ON PART D - NCDOT REQUESTS: Property owner authorization/notification for JD requests associated with North Carolina Department of Transportation (NCDOT) projects will be conducted according to the current NCDOT/USACE protocols. NOTE TO USDA PROGRAM PARTICIPANTS: A Corps approved or preliminary JD may not be valid for the wetland conservation provisions of the Food Security Act of 1985. If you or your tenant are USDA Program participants, or anticipate participation in USDA programs, you should also request a certified wetland determination from the local office of the Natural Resources Conservation Service, prior to starting work. Version: May 2017 Page 1 Jurisdictional Determination Request A. PARCEL INFORMATION Street Address: Multiple City, State: County: Hickory, NC Catawba and Burke Parcel Index Number(s) (PIN): See attachment B. REQUESTOR INFORMATION Name: Ryan Elliott Mailing Address: 706 Hillsborough St. Raleigh, NC 27603 Telephone Number: (919) 773-8887 ext. 125 Electronic Mail Address: ryan.elliott@tgsengineers.com Select one: ❑ I am the current property owner. ❑ I am an Authorized Agent or Environmental Consultant' ❑ Interested Buyer or Under Contract to Purchase ❑� Other, please explain. City and federally funded project C. PROPERTY OWNER INFORMATION Name: See attachment Mailing Address: Telephone Number: Electronic Mail Address: 1 Must provide completed Agent Authorization Form/Letter. 2 Documentation of ownership also needs to be provided with request (copy of Deed, County GIS/Parcel/Tax Record). Version: May 2017 Page 2 Jurisdictional Determination Request D. PROPERTY ACCESS CERTIFICATION' 4 By signing below, I authorize representatives of the Wilmington District, U.S. Army Corps of Engineers (Corps) to enter upon the property herein described for the purpose of conducting on - site investigations, if necessary, and issuing a jurisdictional determination pursuant to Section 404 of the Clean Water Act and/or Section 10 of the Rivers and Harbors Act of 1899. I, the undersigned, am either a duly authorized owner of record of the property identified herein, or acting as the duly authorized agent of the owner of record of the property. Ryan Elliott Print Name Capacity: ❑ Owner ❑�% Authorized Agents 2/28/2020 Date E. REASON FOR JD REQUEST: (Check as many as applicable) ❑ I intend to construct/develop a project or perform activities on this parcel which would be designed to avoid all aquatic resources. ❑ I intend to construct/develop a project or perform activities on this parcel which would be designed to avoid all jurisdictional aquatic resources under Corps authority. ❑✓ I intend to construct/develop a projector perform activities on this parcel which may require authorization from the Corps, and the JD would be used to avoid and minimize impacts to jurisdictional aquatic resources and as an initial step in a future permitting process. I intend to construct/develop a project or perform activities on this parcel which may require authorization from the Corps; this request is accompanied by my permit application and the JD is to be used in the permitting process. ❑ I intend to construct/develop a project or perform activities in a navigable water of the U.S. which is included on the district Section 10 list and/or is subject to the ebb and flow of the tide. A Corps JD is required in order obtain my local/state authorization. I intend to contest jurisdiction over a particular aquatic resource and request the Corps confirm that jurisdiction does/does not exist over the aquatic resource on the parcel. HI believe that the site may be comprised entirely of dry land. v Other: For NCDOT requests following the current NCDOT/USACE protocols, skip to Part E. If there are multiple parcels owned by different parties, please provide the following for each additional parcel on a continuation sheet. 5 Must provide agent authorization form/letter signed by owner(s). Version: May 2017 Page 3 Jurisdictional Determination Request F. JURISDICTIONAL DETERMINATION (JD) TYPE (Select One) 7 I am requesting that the Corps provide a preliminary JD for the property identified herein. A Preliminary Jurisdictional Determination (PJD) provides an indication that there may be "waters of the United States" or "navigable waters of the United States"on a property. PJDs are sufficient as the basis for permit decisions. For the purposes of permitting, all waters and wetlands on the property will be treated as if they are jurisdictional "waters of the United States". PJDs cannot be appealed (33 C.F.R. 331.2); however, a PJD is "preliminary" in the sense that an approved JD can be requested at any time. PJDs do not expire. ❑ I am requesting that the Corps provide an approved JD for the property identified herein. An Approved Jurisdictional Determination (AJD) is a determination that jurisdictional "waters of the United States" or "navigable waters of the United States" are either present or absent on a site. An approved JD identifies the limits of waters on a site determined to be jurisdictional under the Clean Water Act and/or Rivers and Harbors Act. Approved JDs are sufficient as the basis for permit decisions. AJDs are appealable (33 C.F.R. 331.2). The results of the AJD will be posted on the Corps website. A landowner, permit applicant, or other "affected party" (33 C.F.R. 331.2) who receives an AJD may rely upon the AJD for five years (subject to certain limited exceptions explained in Regulatory Guidance Letter 05- 02). I am unclear as to which JD I would like to request and require additional information to inform my decision. G. ALL REQUESTS ❑ Map of Property or Project Area. This Map must clearly depict the boundaries of the review area. ✓❑ Size of Property or Review Area 67 acres. ❑✓ The property boundary (or review area boundary) is clearly physically marked on the site. Version: May 2017 Page 4 Jurisdictional Determination Request H. REQUESTS FROM CONSULTANTS Project Coordinates (Decimal Degrees): Latitude: Longitude 35.744891 ON 81.372268°W ❑� A legible delineation map depicting the aquatic resources and the property/review area. Delineation maps must be no larger than I1x17 and should contain the following: (Corps signature of submitted survey plats will occur after the submitted delineation map has been reviewed and approved).6 ■ North Arrow ■ Graphical Scale ■ Boundary of Review Area ■ Date ■ Location of data points for each Wetland Determination Data Form or tributary assessment reach. For Approved Jurisdictional Determinations: ■ Jurisdictional wetland features should be labeled as Wetland Waters of the US, 404 wetlands, etc. Please include the acreage of these features. ■ Jurisdictional non -wetland features (i.e. tidal/navigable waters, tributaries, impoundments) should be labeled as Non -Wetland Waters of the US, stream, tributary, open water, relatively permanent water, pond, etc. Please include the acreage or linear length of each of these features as appropriate. ■ Isolated waters, waters that lack a significant nexus to navigable waters, or non - jurisdictional upland features should be identified as Non -Jurisdictional. Please include a justification in the label regarding why the feature is non jurisdictional (i.e. "Isolated", "No Significant Nexus", or "Upland Feature"). Please include the acreage or linear length of these features as appropriate. For Preliminary Jurisdictional Determinations: Wetland and non -wetland features should not be identified as Jurisdictional, 404, Waters of the United States, or anything that implies jurisdiction. These features can be identified as Potential Waters of the United States, Potential Non -wetland Waters of the United States, wetland, stream, open water, etc. Please include the acreage and linear length of these features as appropriate. aCompleted Wetland Determination Data Forms for appropriate region (at least one wetland and one upland form needs to be completed for each wetland type) 6 Please refer to the guidance document titled "Survey Standards for Jurisdictional Determinations" to ensure that the supplied map meets the necessary mapping standards. http://www.saw.usace.army.mil/Missions/Re ug latory-Permit- Pro,gram/Juri sdiction/ Version: May 2017 Page 5 Jurisdictional Determination Request aCompleted appropriate Jurisdictional Determination form • PJDs, please complete a Preliminary Jurisdictional Determination Form' and include the Aquatic Resource Table • AJDs, please complete an Approved Jurisdictional Determination Form' O Vicinity Map Aerial Photograph USGS Topographic Map Soil Survey Map Other Maps, as appropriate (e.g. National Wetland Inventory Map, Proposed Site Plan, previous delineation maps, LIDAR maps, FEMA floodplain maps) ❑ Landscape Photos (if taken) aNCSAM and/or NCWAM Assessment Forms and Rating Sheets NC Division of Water Resources Stream Identification Forms Other Assessment Forms ' www.saw.usace.army.mil/Portals/59/docs/re ugulatorregdocs/JD/RGL_08-02_App_A_Prelim_ JD_ Form_fillable.pdf ' Please see http://www.saw.usace.arLny.mil/Missions/Re ugulatory-Permit-Program/Jurisdiction/ Principal Purpose: The information that you provide will be used in evaluating your request to determine whether there are any aquatic resources within the project area subject to federal jurisdiction under the regulatory authorities referenced above. Routine Uses: This information may be shared with the Department of Justice and other federal, state, and local government agencies, and the public, and may be made available as part of a public notice as required by federal law. Your name and property location where federal jurisdiction is to be determined will be included in the approved jurisdictional determination (AJD), which will be made available to the public on the District's website and on the Headquarters USAGE website. Disclosure: Submission of requested information is voluntary; however, if information is not provided, the request for an AJD cannot be evaluated nor can an AJD be issued. Version: May 2017 Page 6 Name: City of Hickory Mailing Address: P.O. Box 398 Hickory, NC 28601 Parcel ID: 2793241259 Telephone Number: (828) 764-9000 Electronic Mail Address: gis@burkenc.org Name: Outbox Hickory LLC Mailing Address: 1920 Cleveland Ave. Charlotte, NC 28203-4881 Parcel ID: 279311654665 & 279311569128 Telephone Number: (828) 327-8484 Electronic Mail Address: hickory@outboxselfstorage.com Name: Jag Properties LLC Mailing Address: 1303 N. Center Street Hickory, NC 28601-2535 Parcel ID: 279311664077 Telephone Number: N/A Electronic Mail Address: N/A Name: Summit Offices Owners Association Mailing Address: P.O. Box 729 Hickory, NC 28603-0729 Parcel ID: 279311655722 Telephone Number: N/A Electronic Mail Address: N/A