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HomeMy WebLinkAboutU-5996_R-5720_PJD-DraftSTATE OF NORTH CAROLINA DEPARTMENT OF TRANSPORTATION ROY COOPF,R C�VF.RN(lR rAMF,S H. TROGDON, YYY SF.CRF.TARY September 25, 2018 U.S. Army Corps of Engineers Washington Regulatory Fie1d Office 2407 West St'' St. Washington, NC 27889-1000 ATTN Subj ect: Dear Sir: Mr. Eric Alsmeyer, NCDOT Regulatory Coordinator Request for a Preliminary rurisdictional Determination for U-5996 (widening Old Carriage Road) and R-5720 (widening Eastern Avenue), Nash County, NC The North Carolina Department of Transportation (NCDOT) proposes to widen Old Carriage Road (S.R. 1603) from Eastern Avenue (S.R. 1770) to Crreen Hills Road (S.R. 1601) for a length of approximately 1.4 miles (STiP U-5996). Additionally, NCDOT proposes to widen Eastern Avenue (S.R. 1770) from Red Oak Road (S.R. 1003) to Old Carriage Road (S.R. 1603) for a length of approximately 2.4 miles (STiP R-5720). Both projects are located adjacent to each other in Nash County (Figures 1 and 2). The study area for this section of the project contains three streams, one tributary, five riparian wetlands, and three ponds. The three ponds, PA, PB, and PC, do not appear to have any connections to jurisdictional features. Enclosed with this request is the Preliminary Jurisdictional Determination Form, vicinity map, topographic map, wetland and stream delineation map, NCDWR Stream identification Forms, NCSAM Forms, USACE Wetland Determination Forms, and NCWAM Forms. We would like to request a site visit to confirm these features. Sean Murray from VHB will be coordinating the site visit meeting. Sincerely, DocuSigned by: c�.a�. %�wS FA DF 361A8$464... Cha oggins Division Environmental Officer Mailin� Address � NC DRPARTMRNT OF TRANSPORTATTON DiVTST(�NF(�iJR F.NVTR(�NMF.NTAT, POST OFFTCR ROX 3165 WTT,SON. NC 27R95 Telephnne�(252)Eu40-6427 Cv�stnmer.Service� 1-R77-36R-496R WehsitP• www.ncdot.gov T,ncatinn � 509 WARD RT,UD WTTSON, NC 27R95 Appendix 2- PRELIMINARY JURISDICTIONAL DETERMINATION (PJD) FORM BACKGROUND INFORMATION A. REPORT COMPLETION DATE FOR PJD: B. NAME AND ADDRESS OF PERSON REQUESTING PJD: chad Coggins, NCDOT Division 4, 509 Ward Blvd. PO Box 3165, Wilson, NC 27895 C. DISTRICT OFFICE, FILE NAME, AND NUMBER: D. PROJECT LOCATION(S) AND BACKGROUND INFORMATION: (USE THE TABLE BELOW TO DOCUMENT MULTIPLE AQUATIC RESOURCES AND/OR AQUATIC RESOURCES AT DIFFERENT SITES) State: NC County/parish/borough: NaSh City: Center coordinates of site (lat/long in degree decimal format): �at.: 35.971154 �ong.: -77.904129 Universal Transverse Mercator: S� 7 Name of nearest waterbody: StOrly Cr22k E. REVIEW PERFORMED FOR SITE EVALUATION (CHECK ALL THAT APPLY): ❑ OfFice (Desk) Determination. Date: ❑ Field Determination. Date(s): TABLE OF AQUATIC RESOURCES IN REVIEW AREA WHICH "MAY BE" SUBJECT TO REGULATORY JURISDICTION. Site Latitude Longitude Estimated amount Type of aquatic Geographic authority number (decimal (decimal of aquatic resource resource (i.e., wetland to which the aquatic degrees) degrees) in review area vs. non-wetland resource "may be" (acreage and linear waters) subject (i.e., Section feet, if applicable) 404 or Section 10/404) Please see attached table. 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 orjudicial 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: � 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: USGS US Topo 7.5' Nashville, NC � Natural Resources Conservation Service Soil Survey. Citation: USDA/NRCS Web Soil Survey �■ National wetlands inventory map(s). Cite name: GIS data, USFWS, NWI website � State/local wetland inventory map(s): � FEMA/FIRM maps: ❑ 100-year Floodplain Elevation is: .(National Geodetic Vertical Datum of 1929) � Photographs: � Aerial (Name & Date): or � Other (Name & Date): � Previous determination(s). File no. and date of response letter: � Other information (please specify): IMPORTANT NOTE: The information recorded on this form has not necessarilv been verified bv the Corps and should not be relied upon for later iurisdictional determinations. Signature and date of Regulatory stafF member completing PJD DocuSigned by: �� ���5 10/15/2018 Signa ure an date of person requesting PJD (REQUIRED, unless obtaining the signature is impracticable)' ' Districts may establish timeframes for requestor to return signed PJD forms. If the requestor 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. Estimated Amount of Site Latitude Longitude Cowardin Aquatic Resource in Class of Aquatic Number (xx.xxxxx) (-xx.xxxxx) Class the Review Area Resource (lin. ft or ac) Isolated Pond PA 35.970529 -77.934532 PUB 0.33 ac. Not regulated under CWA Section 404 Isolated Pond PB 35.970558 -77.933612 PUB 0.14 ac. Not regulated under CWA Section 404 Isolated Pond PC 35.970788 -77.920924 PUB 0.02 ac. Not regulated under CWA Section 404 SA 35.971138 -77.982931 R3UB 161 lin. ft. Perennial Non-Section 10 SB 35.980589 -77.931728 R3UB 352 lin. ft. Perennial Non-Section 10 Stony Creek 35.988690 -77.901477 R3U6 328 lin. ft. Perennial Non-Section 10 TA 35.970293 -77915492 PEM 0.02 ac. Riparian Wetland Non-Section 10 WA 35.971106 -77.931769 PFO 0.17 ac. Riparian Wetland Non-Section 10 WB 35.988690 -77.901477 PFO 0.57 ac. Riparian Wetland Non-Section 10 WC 35.989103 -77.902843 PFO 0.71 ac. Riparian Wetland Non-Section 10 WD 35.989693 -77.902583 PFO 0.42 ac. 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" ' i I�' � �ia Soil Mappnig Unit QStudy Area (182 Ac) w� �I � ,�., i r,,'` �� �'„� _ Bb - Bibb loam, 0-2% slopes, frequently flooded Nu6 - Norfolk-Urban land complex, 0-6% slopes �_____� _+ _� �. ,�� ,� Bo6 - Bonneau loamy sand, 0-4% slopes RaA - Rains fine sandy loam, 0-2% slopes, Southern Coastal Plain �_____� Figure Index '��_• , `� �, �� � GeC - Georgeville loam, 6-10% slopes Ud - Udorthents, loamy � Soil Unit Boundary �j, - �'a: ' � � � �- " - GrC - Gritney sandy loam, 6-10% slopes `— ; ` _ � sca�e FIGURE 4-1 U-5996/R-5720 ���Qi�°�� o �oo zoo aoo Old Carriage Road and Eastern Avenue �� �� Feet e Nash County Soils Map Nash County �I7��, �V,86 I' � -- h,,;,,o Rocky Mount � � , ��� i � � � :54�`�III .i �� � � ' ��1' III I��F/�I , r�,,� . l,��q ' � �' y?!�I�I'IIY T ;. �v r�M' ,,, � u, �!�. 4"�'� �N�i���, � � d ; r � I • _ ,tT � � i � '� �� �` , - �� � • ��� � I � r,� ;� : • ;.�rt . �;"�'��� I �, ��,. :'� i ' � � � ���' r .. � �`�� I� i� _ �. � :. "5 � � • .. � � � �� � � � � ,;i� . �' i � �. � i t, i' � i � Study Area (182 Ac) �_____j Figure Index � Soil Unit Boundary Scale 0 100 200 400 e Feet � ,� r � �� - � ..-.-_ _ � „ e , ,w -, , � �� � � � .. � e, I + ► � `:S'�^ � � � I �� � j '; " ,� �_ '{` :�> �r I ~ �� f' � I :� �� � _ .rb�Y _ � rf� � :�t.�� . . � . I t���'� I � , � 'N� � . � �r I� �� '1 ' � : �'�� � j • '��-�_. T �� � I 1 � �;: � _ . o'� �"�." _� �: �„°�"�1���`,,, 'i � .,,�, ,� -�, a� �' I '�� � � � � i �� . - � � i '�" � � .��"�� � �� � ��'i L�, � � y, • '� �' �I � �� ,�i*� �� � � `1 � �� � . . � � -1- � �� �I� � � � ,,� . . '; '�` a f��.� ° � ��" i� � • � i _ '�,� � i i , i i — y � �� � � , i � i �� , � �_ - +� � •` � �� � I _ {.;�� 1� � ' � , �� �- _.r � �y� � li � I �i � ,T' { •w � I J ' jI� � a � 1, �,�1� �II � � I � *��� , �. ' �4� ^� ����� � � d�- �. � � �' r � � � 'y -.� . .L�, �. . � A � -' r����� h � � � � ��� � �j �Y r " � , � r'f e-�'. } )� � _- 4� n _-_�+ s . � . � ��� • � �' �'� r A i �� ��1j } 4 � �,' f ��� , �� y�l I� ���j i ,;�1 �� 7�.� .�!f�_- —,1-- . Q � T�' . ' �. � ��`� ����_ � Soil Mappnig Unit ` �� �' �" Bb - Bibb loam, 0-2% slopes, frequently flooded No6 - Norfolk loamy sand, 2-6% slopes ���a'ti� ,� ` Bo6 - Bonneau loamy sand, 0-4% slopes Nu6 - Norfolk-Urban land complex, 0-6% slopes `t �,� "' ' Gr6 - Gritney sandy loam, 2-6% slopes RaA - Rains fine sandy loam, 0-2% slopes, Southern Coastal Plain '` �' k� _ " GrC - Gritney sandy loam, 6-10% slopes W- Water l�;` �.` � NoA - Norfolk loamy sand, 0-2% slopes �. ��' ��, A� FIGURE 4-2 U-5996/R-5720 `�+,��^� Old Carriage Road and Eastern Avenue -� �; Nash County Soils Map Nash County �I7��, Red Oak �,,, ���,_ �<��.� �,� �� ' 'y.l �.J - �4 � 1 .`�" `� _ r i - ��� T ��},��T ri!^1 ROCky`MOunt �,���� _x� `�?r. Yy♦ I �. 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" �""�`� �' �'.�" Wetland .�� k ;�7"�� � - �w - _ `-;� . - — - , _ � y,�_ ,� �„� r y ; , "'"�- � _ ,� - '.�- _ - ��` �.� • _ _ `�, ;, � �� _�Y .. , : _ � � .e = � , � �: -- � _- - Sb j `'�1� . `.�' ; � - �t.. _ Perennial Stream �� -� � �'�'< '"� � r , - � . �r� �#. � �. � � �� a�,� r � � ` -, . �.�r,' �i-. '� '�►' ' r •1 L _ ,,,_' . � .� , �- � �� � � . - - `� y F. � � �-> 1. .��_ _ ,+ j, i+ �, _ Pond � ��dc:. � ; ,�� ��,�; �_ _ . �� -� _w�.°� ,,,r �� �-' � -� ,;,,».� �� _�( � � �: �.�.� '`'1� { E ' � `r;� � � ' `v - �' - -.. - - w '�.i.y :. 1 � 't.. y 4- _ � `J � � t,. . ' �: ,y� '.,: _ Tributary �y � s v.� _ � . ��-.'�,"'_ • :� �. Y���`-� �`' - � . 4 ; � �' ,_ _ = F �. - -. _ `` �r; - - . � o r�ia�ion &�ialY��s.� � � "i� � NC Ce��cr foi �Gcogiaohi�c I� sca�e FIGURE 6-7 U-5996/R-5720 �����io' o �oo zoo aoo Old Carriage Road and Eastern Avenue �� Feet Jurisdictional Features (Aerial Basemap) Nash County �I7��, � April30 2018 April30 2018 April 30, 2018 April30 20"I8 April 30, 2018 AF�ril30 2018 April30 2018 f, F r�� r �� � r NC Divisian of VVater Quality -fl�ethodology foe� Identificaiion of intermitten� and Perennial Sfreams and Their Origins v. 4.11 Date: Evaluator: Stream Identi�cation Form Version 4.11 Total Points: Stream is at least intermittent if>_ 19 or perennia! if? 30" 4� -/ �_ � / �. m� Project/Site County: /s - '���r'%J s�„ fr Stream Determination (c Ephemeral Intermittent Laiitude: r' � P`� �;� � � �( Longitude: � � � `(I_� � �� �r'�q•' ,, c�n� Other � yr �,� � ., ,' f � ,, nnla e.g. Quad 1�Iarhe � ` � �- , ' A. Geomor holo (Subtotal = i`� `<> } Aflsent Weak IUloderate Strong 1 a Continuity of chan�el bed and bank ` 0 1 2 2. Sinuosi#y of channel along thalweg 0 1 ;'2� `"3 3. In-channel structure: ex. riffle-pool, step-pool, 0 1 (2� 3 ri le- ool se uence - 4. Pa�ticle size of stream substrate 0 1 ( 2� 3 5. Active/relict floodplain 0 1 ;``2� 3 6. Depositional bars or benches 0 1 � !�� 7. Recent alluvial deposits 0 1 r''2 ;� 3 8. Headcuts 0 11 � ' 2 3 9. Grade control 0 0.5 ' 1;'� 1.5 10. Natural valley 0 ` 0.5� 1 1.5 11. Second or greater order channel No = 0 � Yes 3"� e artificial ditches are not rated; see discussions in manual B. Hydrology (Subtotal = � � ) 12. Presence of Baseflow 13. Iron oxidizing bacteria 14. Leaf iitfer 15. Sediment on plants or debris _ 16. Organic debris lines or piles 17. Soil-based evidence of high water tak C. Biology (Subtotal = �� ) 18. Fibrous roots in streambed 19. Rooted upland plants in streambed 20. Macrobenthos (note diversity and abund 21. Aquatic Moilusks 22. Fish 23. Crayfish 24. Amphibians 25. Algae 26. Wetland plants in streambed *perennial streams may also be identified usir NOt@S:''(,�l1 r�,��',fc •�-',�. '`,r=+aFv'rksa6" r � No=O Ci7 � C�] other methods. See p. 35 of manual. ) �. rV�1', - �����':..._ . Sketch: � �� `� ���' / j � � � � , ��,, _ ___ . �„-- - -- � ---- ---- � 41 1 0.5 2 2 1 1 0.5 Q.5 2 2 0.5 1 1 2 1 1 1 e FACW = 0.75; OBL = 1.5 Other = 0 3 0 1.5 1.5 0 0 3 3 1.5 1.5 1.5 1.5 NC SAM FIELD ASSESSMENT RESULTS Accompanies User Manual Version 2.1 USACE AID #: NCDWR #: INSTRUCTIONS: Attach a sketch of the assessment area and photographs. Attach a copy of the USGS 7.5-minute topographic quadrangle, and circle the location of the stream reach under evaluation. If multiple stream reaches will be evaluated on the same property, identify and number all reaches on the attached map, and include a separate form for each reach. See the NC SAM User Manual for detailed descriptions and explanations of requested information. Record in the "Notes/Sketch" section if supplementary measurements were performed. See the NC SAM User Manual for examples of additional measurements that may be relevant. NOTE EVIDENCE OF STRESSORS AFFECTING THE ASSESSMENT AREA (do not need to be within the assessment area). PROJECT/SITE INFORMATION: 1. Project name (if any): Creedmoor Road 2. Date of evaluation: 4/19/2018 3. ApplicanUowner name: NCDOT 4. Assessor name/organization: Sean Murray, VHB 5. County: Wake 6. Nearest named water body 7. River basin: Tar-Pamlico on USGS 7.5-minute quad: Stony Creek 8. Site coordinates (decimal degrees, at lower end of assessment reach): 35.988663/-77.900763 STREAM INFORMATION: (depth and width can be approximations) 9. Site number (show on attached map): Stony Creek 10. Length of assessment reach evaluated (feet): 300 11. Channel depth from bed (in rifFle, if present) to top of bank (feet): 5 ❑Unable to assess channel depth. 12. Channel width at top of bank (feet): 40 13. Is assessment reach a swamp steam? ❑Yes ❑No 14. Feature type: �Perennial flow ❑Intermittent flow ❑Tidal Marsh Stream STREAM CATEGORY INFORMATION: 15. NC SAM Zone: ❑ Mountains (M) � Piedmont (P) ❑ Inner Coastal Plain (I) ❑ Outer Coastal Plain (0) 16. Estimated geomorphic �A ��� valley shape (skip for Tidal Marsh Stream): (more sinuous stream, flatter valley slope) ❑B (less sinuous stream, steeper valley slope) 17. Watershed size: (skip ❑Size 1(< 0.1 miz) ❑Size 2(0.1 to < 0.5 miz) ❑Size 3(0.5 to < 5 miz) �Size 4(>_ 5 miz) for Tidal Marsh Stream) ADDITIONAL INFORMATION: 18. Were regulatory considerations evaluated? �Yes ❑No If Yes, check all that apply to the assessment area. ❑Section 10 water ❑Classified Trout Waters ❑Water Supply Watershed (❑I ❑II ❑III ❑IV ❑V) ❑Essential Fish Habitat ❑Primary Nursery Area ❑ High Quality Waters/Outstanding Resource Waters ❑Publicly owned property �NCDWR Riparian buffer rule in effect ❑Nutrient Sensitive Waters ❑Anadromous fish ❑303(d) List ❑CAMA Area of Environmental Concern (AEC) ❑Documented presence of a federal and/or state listed protected species within the assessment area. List species: ❑Designated Critical Habitat (list species) 19. Are additional stream information/sunolementarv measurements included in "Notes/Sketch" section or attached? IRIYes I-lNo 1. Channel Water - assessment reach metric (skip for Size 1 streams and Tidal Marsh Streams) �A Water throughout assessment reach. ❑B No flow, water in pools only. ❑C No water in assessment reach. 2. Evidence of Flow Restriction - assessment reach metric ❑A At least 10% of assessment reach in-stream habitat or riffle-pool sequence is severely affected by a flow restriction or fill to the point of obstructing flow or a channel choked with aquatic macrophytes or ponded water or impoundment on flood or ebb within the assessment reach (examples: undersized or perched culverts, causeways that constrict the channel, tidal gates, debris jams, beaver dams). �B NotA 3. Feature Pattern - assessment reach metric ❑A A majority of the assessment reach has altered pattern (examples: straightening, modification above or below culvert). �B NotA 4. Feature Longitudinal Profile - assessment reach metric ❑A Majority of assessment reach has a substantially altered stream profile (examples: channel down-cutting, existing damming, over widening, active aggradation, dredging, and excavation where appropriate channel profile has not reformed from any of these disturbances). �B NotA 5. Signs of Active Instability - assessment reach metric Consider only current instability, not past events from which the stream has currently recovered. Examples of instability include active bank failure, active channel down-cutting (head-cut), active widening, and artificial hardening (such as concrete, gabion, rip-rap). �A < 10% of channel unstable ❑B 10 to 25% of channel unstable ❑C > 25% of channel unstable 6. Streamside Area Interaction — streamside area metric Consider for the Left Bank (LB) and the Right Bank (RB). LB RB ❑A ❑A Little or no evidence of conditions that adversely affect reference interaction ❑B �B Moderate evidence of conditions (examples: berms, levees, down-cutting, aggradation, dredging) that adversely affect reference interaction (examples: limited streamside area access, disruption of flood flows through streamside area, leaky or intermittent bulkheads, causeways with floodplain constriction, minor ditching [including mosquito ditching]) �C ❑C Extensive evidence of conditions that adversely affect reference interaction (little to no floodplain/intertidal zone access [examples: causeways with floodplain and channel constriction, bulkheads, retaining walls, fill, stream incision, disruption of flood flows through streamside area] or too much floodplain/intertidal zone access [examples: impoundments, intensive mosquito ditching]) or floodplain/intertidal zone unnaturally absent or assessment reach is a man-made feature on an interstream divide Water Quality Stressors — assessment reach/intertidal zone metric Check all that apply. �A Discolored water in stream or intertidal zone (milky white, blue, unnatural water discoloration, oil sheen, stream foam) �B Excessive sedimentation (burying of stream features or intertidal zone) ❑C Noticeable evidence of pollutant discharges entering the assessment reach and causing a water quality problem ❑D Odor (not including natural sulfide odors) ❑E Current published or collected data indicating degraded water quality in the assessment reach. Cite source in "Notes/Sketch" section. ❑F Livestock with access to stream or intertidal zone ❑G Excessive algae in stream or intertidal zone ❑H Degraded marsh vegetation in the intertidal zone (removal, burning, regular mowing, destruction, etc) ❑I Other: (explain in "Notes/Sketch" section) ❑J Little to no stressors 8. Recent Weather — watershed metric (skip for Tidal Marsh Streams) For Size 1 or 2 streams, D1 drought or higher is considered a drought; for Size 3 or 4 streams, D2 drought or higher is considered a drought. ❑A Drought conditions and no rainfall or rainfall not exceeding 1 inch within the last 48 hours ❑B Drought conditions and rainfall exceeding 1 inch within the last 48 hours �C No drought conditions 9. Large or Dangerous Stream — assessment reach metric ❑Yes �No Is stream is too large or dangerous to assess? If Yes, skip to Metric 13 (Streamside Area Ground Surface Condition). 10. Natural In-stream Habitat Types — assessment reach metric 10a. �Yes ❑No Degraded in-stream habitat over majority of the assessment reach (examples of stressors include excessive sedimentation, mining, excavation, in-stream hardening [for example, rip-rap], recent dredging, and snagging) (evaluate for Size 4 Coastal Plain streams only, then skip to Metric 12) 10b. Check all that occur (occurs if > 5% coverage of assessment reach) (skip for Size 4 Coastal Plain streams) ❑A Multiple aquatic macrophytes and aquatic mosses m�, ❑F 5% oysters or other natural hard bottoms (include liverworts, lichens, and algal mats) � m ❑G Submerged aquatic vegetation ❑B Multiple sticks and/or leaf packs and/or emergent g Y ❑H Low-tide refugia (pools) vegetation Y L ❑I Sand bottom �C Multiple snags and logs (including lap trees) L@ ❑J 5% vertical bank along the marsh �D 5% undercut banks and/or root mats and/or roots �� ❑K Little or no habitat in banks extend to the normal wetted perimeter ❑E Little or no habitat *********************************REMAINING QUESTIONS ARE NOT APPLICABLE FOR TIDAL MARSH STREAMS**************************** 11. Bedform and Substrate — assessment reach metric (skip for Size 4 Coastal Plain streams and Tidal Marsh Streams) 11a. ❑Yes �No Is assessment reach in a natural sand-bed stream? (skip for Coastal Plain streams) 11 b. Bedform evaluated. Check the appropriate box(es). ❑A Riffle-run section (evaluate 11c) �B Pool-glide section (evaluate 11d) ❑C Natural bedform absent (skip to Metric 12, Aquatic Life) 11 c. In riffle sections, check all that occur below the normal wetted perimeter of the assessment reach — whether or not submerged. Check at least one box in each row (skip for Size 4 Coastal Plain streams and Tidal Marsh Streams). Not Present (NP) = absent, Rare (R) = present but < 10%, Common (C) _> 10-40%, Abundant (A) _> 40-70%, Predominant (P) _> 70%. Cumulative percentages should not exceed 100% for each assessment reach. NP R C A P ❑ ❑ ❑ ❑ ❑ Bedrock/saprolite ❑ ❑ ❑ ❑ ❑ Boulder (256 — 4096 mm) ❑ ❑ ❑ ❑ ❑ Cobble (64 — 256 mm) ❑ ❑ ❑ ❑ ❑ Gravel (2 — 64 mm) ❑ ❑ ❑ ❑ ❑ Sand (.062 — 2 mm) ❑ ❑ ❑ ❑ ❑ SilUclay (< 0.062 mm) ❑ ❑ ❑ ❑ ❑ Detritus ❑ ❑ ❑ ❑ ❑ Artificial (rip-rap, concrete, etc.) 11d. ❑Yes �No Are pools filled with sediment? (skip for Size 4 Coastal Plain streams and Tidal Marsh Streams) 12. Aquatic Life — assessment reach metric (skip for Tidal Marsh Streams) 12a. �Yes ❑No Was an in-stream aquatic life assessment performed as described in the User Manual? If No, select one of the following reasons and skip to Metric 13. ❑No Water ❑Other: 12b. �Yes ❑No Are aquatic organisms present in the assessment reach (look in riffles, pools, then snags)? If Yes, check all that apply. If No, skip to Metric 13. 1 >1 Numbers over columns refer to "individuals" for Size 1 and 2 streams and "taxa" for Size 3 and 4 streams. ❑ �Adult frogs ❑ ❑Aquatic reptiles ❑ ❑Aquatic macrophytes and aquatic mosses (include liverworts, lichens, and algal mats) ❑ ❑Beetles ❑ ❑Caddisfly larvae (T) ❑ ❑Asian clam (Corbicula) ❑ �Crustacean (isopod/amphipod/crayfish/shrimp) ❑ �Damselfly and dragonfly larvae ❑ ❑Dipterans ❑ ❑Mayfly larvae (E) ❑ ❑Megaloptera (alderFly, fishfly, dobsonfly larvae) ❑ ❑Midges/mosquito larvae ❑ �Mosquito fish (Gambusia) or mud minnows (Umbra pygmaea) ❑ ❑Mussels/Clams (not Corbicula) ❑ �Other fish ❑ �Salamanders/tadpoles ❑ �Snails ❑ ❑Stonefly larvae (P) ❑ ❑Tipulid larvae ❑ ❑Worms/leeches 13. Streamside Area Ground Surface Condition — streamside area metric (skip for Tidal Marsh Streams and B valley types) Consider for the Left Bank (LB) and the Right Bank (RB). Consider storage capacity with regard to both overbank flow and upland runoff. LB RB ❑A ❑A Little or no alteration to water storage capacity over a majority of the streamside area �B �B Moderate alteration to water storage capacity over a majority of the streamside area ❑C ❑C Severe alteration to water storage capacity over a majority of the streamside area (examples: ditches, fill, soil compaction, livestock disturbance, buildings, man-made levees, drainage pipes) 14. Streamside Area Water Storage — streamside area metric (skip for Size 1 streams, Tidal Marsh Streams, and B valley types) Consider for the Left Bank (LB) and the Right Bank (RB) of the streamside area. LB RB ❑A �A Majority of streamside area with depressions able to pond water >_ 6 inches deep �B ❑B Majority of streamside area with depressions able to pond water 3 to 6 inches deep ❑C ❑C Majority of streamside area with depressions able to pond water < 3 inches deep 15. Wetland Presence — streamside area metric (skip for Tidal Marsh Streams) Consider for the Left Bank (LB) and the Right Bank (RB). Do not consider wetlands outside of the streamside area or within the normal wetted perimeter of assessment reach. LB RB �Y �Y Are wetlands present in the streamside area? ❑N ❑N 16. Baseflow Contributors — assessment reach metric (skip for Size 4 streams and Tidal Marsh Streams) Check all contributors within the assessment reach or within view of and draining to the assessment reach. �A Streams and/or springs Qurisdictional discharges) ❑B Ponds (include wet detention basins; do not include sediment basins or dry detention basins) ❑C Obstruction passing flow during low-flow periods within the assessment area (beaver dam, leaky dam, bottom-release dam, weir) �D Evidence of bank seepage or sweating (iron in water indicates seepage) �E Stream bed or bank soil reduced (dig through deposited sediment if present) ❑F None of the above 17. Baseflow Detractors — assessment area metric (skip for Tidal Marsh Streams) Check all that apply. ❑A Evidence of substantial water withdrawals from the assessment reach (includes areas excavated for pump installation) ❑B Obstruction not passing flow during low-flow periods affecting the assessment reach (ex: watertight dam, sediment deposit) ❑C Urban stream (>_ 24% impervious surface for watershed) ❑D Evidence that the streamside area has been modified resulting in accelerated drainage into the assessment reach ❑E Assessment reach relocated to valley edge �F None of the above 18. Shading — assessment reach metric (skip for Tidal Marsh Streams) Consider aspect. Consider "leaf-on" condition. ❑A Stream shading is appropriate for stream category (may include gaps associated with natural processes) �B Degraded (example: scattered trees) ❑C Stream shading is gone or largely absent 19. Buffer Width — streamside area metric (skip for Tidal Marsh Streams) Consider "vegetated buffer" and "wooded buffer" separately for left bank (LB) and right bank (RB) starting at the top of bank out to the first break. Vegetated Wooded LB RB LB RB ❑A ❑A ❑A ❑A >_ 100 feet wide or extends to the edge of the watershed ❑B �B ❑B �B From 50 to < 100 feet wide ❑C ❑C �C ❑C From 30 to < 50 feet wide �D ❑D ❑D ❑D From 10 to < 30 feet wide ❑E ❑E ❑E ❑E < 10 feet wide or no trees 20. Buffer Structure — streamside area metric (skip for Tidal Marsh Streams) Consider for left bank (LB) and right bank (RB) for Metric 19 ("Vegetated" Buffer Width). LB RB ❑A �A Mature forest ❑B ❑B Non-mature woody vegetation or modified vegetation structure �C ❑C Herbaceous vegetation with or without a strip of trees < 10 feet wide ❑D ❑D Maintained shrubs ❑E ❑E Little or no vegetation 21. Buffer Stressors — streamside area metric (skip for Tidal Marsh Streams) Check all appropriate boxes for left bank (LB) and right bank (RB). Indicate if listed stressor abuts stream (Abuts), does not abut but is within 30 feet of stream (< 30 feet), or is between 30 to 50 feet of stream (30-50 feet). If none of the following stressors occurs on either bank, check here and skip to Metric 22: ❑ Abuts < 30 feet 30-50 feet LB RB LB RB LB RB ❑A ❑A ❑A ❑A ❑A ❑A Row crops �B �B �B �B �B �B Maintained turf ❑C ❑C ❑C ❑C ❑C ❑C Pasture (no livestock)/commercial horticulture ❑D ❑D ❑D ❑D ❑D ❑D Pasture (active livestock use) 22. Stem Density — streamside area metric (skip for Tidal Marsh Streams) Consider for left bank (LB) and right bank (RB) for Metric 19 ("Wooded" Buffer Width). LB RB ❑A �A Medium to high stem density �B ❑B Low stem density ❑C ❑C No wooded riparian buffer or predominantly herbaceous species or bare ground 23. Continuity of Vegetated Buffer — streamside area metric (skip for Tidal Marsh Streams) Consider whether vegetated buffer is continuous along stream (parallel). Breaks are areas lacking vegetation > 10 feet wide. LB RB ❑A �A The total length of buffer breaks is < 25 percent. �B ❑B The total length of buffer breaks is between 25 and 50 percent. ❑C ❑C The total length of buffer breaks is > 50 percent. 24. Vegetative Composition — streamside area metric (skip for Tidal Marsh Streams) Evaluate the dominant vegetation within 100 feet of each bank or to the edge of the watershed (whichever comes first) as it contributes to assessment reach habitat. LB RB ❑A ❑A Vegetation is close to undisturbed in species present and their proportions. Lower strata composed of native species, with non-native invasive species absent or sparse. ❑B �B Vegetation indicates disturbance in terms of species diversity or proportions, but is still largely composed of native species. This may include communities of weedy native species that develop after clear-cutting or clearing or communities with non-native invasive species present, but not dominant, over a large portion of the expected strata or communities missing understory but retaining canopy trees. �C ❑C Vegetation is severely disturbed in terms of species diversity or proportions. Mature canopy is absent or communities with non-native invasive species dominant over a large portion of expected strata or communities composed of planted stands of non-characteristic species or communities inappropriately composed of a single species or no vegetation. 25. Conductivity — assessment reach metric (skip for all Coastal Plain streams) 25a. ❑Yes �No Was conductivity measurement recorded? If No, select one of the following reasons. ❑No Water �Other: 25b. Check the box corresponding to the conductivity measurement (units of microsiemens per centimeter). ❑A < 46 ❑ B 46 to < 67 ❑C 67 to < 79 ❑ D 79 to < 230 ❑ E >_ 230 Notes/Sketch: Assessment reach includes portions of Stony Creek, immediately east and west and under Old Carriage Road. At the road, the bridge construction filled most of the wetland buffer for the creek. The bank on the left side, downstream of the bridge had been mostly cleared for residential development, and a powerline easement had been cleared through the wetland on the right bank. Stream is basically unvegetated. Water had a milky color and oily sheen through most of the reach. Stream Site Name Creedmoor Road Stream Category Pa4 Draft NC SAM Stream Rating Sheet Accompanies User Manual Version 2.1 Date of Assessment 4/19/2018 Assessor Name/Organization Sean Murray, VHB Notes of Field Assessment Form (Y/N) Presence of regulatory considerations (Y/N) Additional stream information/supplementary measurements included (Y/N) NC SAM feature type (perennial, intermittent, Tidal Marsh Stream) Function Class Rating Summary (1) Hydrology (2) Baseflow (2) Flood Flow (3) Streamside Area Attenuation (4) Floodplain Access (4) Wooded Riparian Buffer (4) Microtopography (3) Stream Stability (4) Channel Stability (4) Sediment Transport (4) Stream Geomorphology (2) Stream/Intertidal Zone Interaction (2) Longitudinal Tidal Flow (2) Tidal Marsh Stream Stability (3) Tidal Marsh Channel Stability Tidal Marsh Stream (1) Water Quality (2) Baseflow (2) Streamside Area Vegetation (3) Upland Pollutant Filtration (3) Thermoregulation (2) Indicators of Stressors (2) Aquatic Life Tolerance (2) Intertidal Zone Filtration (1) Habitat (2) In-stream Habitat (3) Baseflow (3) Substrate (3) Stream Stability (3) In-stream Habitat (2) Stream-side Habitat (3) Stream-side Habitat (3) Thermoregulation (2) Tidal Marsh In-stream Habitat a (3) Flow Restriction (3) Tidal Marsh Stream Stability (4) Tidal Marsh Channel Stability (4) Tidal Marsh Stream Geomorphology (3) Tidal Marsh In-stream Habitat (2) Intertidal Zone Overall YES YES YES Perennial USACE/ NCDWR All Streams Intermittent MEDIUM HIGH MEDIUM LOW LOW MEDIUM LOW HIGH HIGH HIGH HIGH NA NA NA NA NA LOW HIGH LOW LOW MEDIUM YES MEDIUM NA HIGH HIGH HIGH HIGH HIGH HIGH MEDIUM MEDIUM MEDIUM NA NA NA NA NA NA NA MEDIUM NC Division of Water Qualiiy -PViethodology �or lden#ification of Interrnifitent and Perennial Sireams and Their Origins v. 4.11 IeTC llWQ Stream Identification Form Version 4.11. Date: �� ;� � , .,-, Project/Site: � �"" � � �� i� i Evaluator: � � � �� � �� � County: � � ��, � 1 �--� Total Points: � ° Stream is at least intermitteni C Stream Determination (circl if>_ 19 oroerennial if? 30" ._.a ���"' �phemeral Intermitten Peren } ... Latitude �' j e �j `�� � � ; ��� Longitude: � � f �'t ,`� .:r `�( ? � Other � � e.g. Quad Name: A. Geomor holo (Subtotal =�' .�� ) Abseni VVeak fl�oderate Strong 1a Continuity of channel bed and bank 0 1 2� 3 2. Sinuosity of channel along thalweg 0 1 2 �3 3. In-channel structure: ex. riffle-pool, step-pool, 0 1 2 � ri le- ool se uence 4. Particle size of stream substrate 0 1 2 3 5. Active/relict floodplain 0 2 3 6. Depositional bars or benches 0 1 2 3 7. Recent alluvial deposits � 2 3 8. Headcuts � Z 3 9. Grade control 0 0.5 1 1.5 10. Natural vailey 0 0.5 1 1.5 11. Second or greater order channel o= Yes = 3 a ��-a GJ PIG IIVI IqIGU� JGG 41JtiUJJ1UIIJ III IIIQIIUtlI B. Hydrology (Subtotal = � ) �2. Presence of Baseflow 13. Iron oxidizing bacteria 14. Leaf litter 15. Sediment on plants or debris 16. Organic debris lines or piles 17. Soil-based evidence of high water table? C. Biology (Subtotal = ) 18. Fibrous roots in streambed 19. Rooted upland plants in streambed 20. MaCrobenthos (note diversity and abundance) 21. Aquatic Mollusks 0 1 0 1 1.5 1 0 0. 0 0.5 No=O 3 2 3 2 22. Fish �6 0.5 23. Crayfish �0 0.5 24. Amphibians 0.5 25. Algae 0 0.5 26. Wetland plants in streambed FACW = 0.75; OBL = "perennial streams may aiso be identified using other methods. See p. 35 of manual. Notes: 7 �ir� �„ �1 � . � �Q �.� ,�� ��'��w� . Sketch: 41 2 2 es = 1 2 2 1 1 1 1 � Other = 0 3 0 1.5 1.5 NC SAM FIELD ASSESSMENT RESULTS Accompanies User Manual Version 2.1 USACE AID #: NCDWR #: INSTRUCTIONS: Attach a sketch of the assessment area and photographs. Attach a copy of the USGS 7.5-minute topographic quadrangle, and circle the location of the stream reach under evaluation. If multiple stream reaches will be evaluated on the same property, identify and number all reaches on the attached map, and include a separate form for each reach. See the NC SAM User Manual for detailed descriptions and explanations of requested information. Record in the "Notes/Sketch" section if supplementary measurements were performed. See the NC SAM User Manual for examples of additional measurements that may be relevant. NOTE EVIDENCE OF STRESSORS AFFECTING THE ASSESSMENT AREA (do not need to be within the assessment area). PROJECT/SITE INFORMATION: U-5996 Eastern Ave and Old 1. Project name (if any): Carriage Rd 2. Date of evaluation: 4/19/2018 3. ApplicanUowner name: NCDOT 4. Assessor name/organization: Sean Murray, VHB 5. County: Nash 6. Nearest named water body 7. River basin: Tar-Pamlico on USGS 7.5-minute quad: Stony Creek 8. Site coordinates (decimal degrees, at lower end of assessment reach): 35.971138/-77.932931 STREAM INFORMATION: (depth and width can be approximations) 9. Site number (show on attached map): SA 10. Length of assessment reach evaluated (feet): 125 11. Channel depth from bed (in riffle, if present) to top of bank (feet): 2 ❑Unable to assess channel depth. 12. Channel width at top of bank (feet): 4 13. Is assessment reach a swamp steam? ❑Yes ❑No 14. Feature type: �Perennial flow ❑Intermittent flow ❑Tidal Marsh Stream STREAM CATEGORY INFORMATION: 15. NC SAM Zone: ❑ Mountains (M) � Piedmont (P) ❑ Inner Coastal Plain (I) ❑ Outer Coastal Plain (0) 16. Estimated geomorphic �AL��� J �B valley shape (skip for Tidal Marsh Stream): (more sinuous stream, flatter valley slope) (less sinuous stream, steeper valley slope) 17. Watershed size: (skip �Size 1(< 0.1 mi2) ❑Size 2(0.1 to < 0.5 mi2) ❑Size 3(0.5 to < 5 mi2) ❑Size 4(>_ 5 mi2) for Tidal Marsh Stream) ADDITIONAL INFORMATION: 18. Were regulatory considerations evaluated? �Yes ❑No If Yes, check all that apply to the assessment area. ❑Section 10 water ❑Classified Trout Waters ❑Water Supply Watershed (❑I ❑II ❑III ❑IV ❑V) ❑Essential Fish Habitat ❑Primary Nursery Area ❑ High Quality Waters/Outstanding Resource Waters ❑Publicly owned property �NCDWR Riparian buffer rule in effect ❑Nutrient Sensitive Waters ❑Anadromous fish ❑303(d) List ❑CAMA Area of Environmental Concern (AEC) ❑Documented presence of a federal and/or state listed protected species within the assessment area. List species: ❑Designated Critical Habitat (list species) 19. Are additional stream information/suoolementarv measurements included in "Notes/Sketch" section or attached? 6aYes I-lNo 1. Channel Water - assessment reach metric (skip for Size 1 streams and Tidal Marsh Streams) �A Water throughout assessment reach. ❑B No flow, water in pools only. ❑C No water in assessment reach. 2. Evidence of Flow Restriction - assessment reach metric ❑A At least 10% of assessment reach in-stream habitat or riffle-pool sequence is severely affected by a flow restriction or fill to the point of obstructing flow or a channel choked with aquatic macrophytes or ponded water or impoundment on flood or ebb within the assessment reach (examples: undersized or perched culverts, causeways that constrict the channel, tidal gates, debris jams, beaver dams). �B NotA 3. Feature Pattern - assessment reach metric ❑A A majority of the assessment reach has altered pattern (examples: straightening, modification above or below culvert). �B NotA 4. Feature Longitudinal Profile - assessment reach metric ❑A Majority of assessment reach has a substantially altered stream profile (examples: channel down-cutting, existing damming, over widening, active aggradation, dredging, and excavation where appropriate channel profile has not reformed from any of these disturbances). �B NotA 5. Signs of Active Instability - assessment reach metric Consider only current instability, not past events from which the stream has currently recovered. Examples of instability include active bank failure, active channel down-cutting (head-cut), active widening, and artificial hardening (such as concrete, gabion, rip-rap). �A < 10% of channel unstable ❑B 10 to 25% of channel unstable ❑C > 25% of channel unstable 6. Streamside Area Interaction — streamside area metric Consider for the Left Bank (LB) and the Right Bank (RB). LB RB ❑A �A Little or no evidence of conditions that adversely affect reference interaction �B ❑B Moderate evidence of conditions (examples: berms, levees, down-cutting, aggradation, dredging) that adversely affect reference interaction (examples: limited streamside area access, disruption of flood flows through streamside area, leaky or intermittent bulkheads, causeways with floodplain constriction, minor ditching [including mosquito ditching]) ❑C ❑C Extensive evidence of conditions that adversely affect reference interaction (little to no floodplain/intertidal zone access [examples: causeways with floodplain and channel constriction, bulkheads, retaining walls, fill, stream incision, disruption of flood flows through streamside area] or too much floodplain/intertidal zone access [examples: impoundments, intensive mosquito ditching]) or floodplain/intertidal zone unnaturally absent or assessment reach is a man-made feature on an interstream divide Water Quality Stressors — assessment reach/intertidal zone metric Check all that apply. ❑A Discolored water in stream or intertidal zone (milky white, blue, unnatural water discoloration, oil sheen, stream foam) ❑B Excessive sedimentation (burying of stream features or intertidal zone) ❑C Noticeable evidence of pollutant discharges entering the assessment reach and causing a water quality problem ❑D Odor (not including natural sulfide odors) ❑E Current published or collected data indicating degraded water quality in the assessment reach. Cite source in "Notes/Sketch" section. ❑F Livestock with access to stream or intertidal zone ❑G Excessive algae in stream or intertidal zone ❑H Degraded marsh vegetation in the intertidal zone (removal, burning, regular mowing, destruction, etc) ❑I Other: (explain in "Notes/Sketch" section) �J Little to no stressors 8. Recent Weather — watershed metric (skip for Tidal Marsh Streams) For Size 1 or 2 streams, D1 drought or higher is considered a drought; for Size 3 or 4 streams, D2 drought or higher is considered a drought. ❑A Drought conditions and no rainfall or rainfall not exceeding 1 inch within the last 48 hours ❑B Drought conditions and rainfall exceeding 1 inch within the last 48 hours �C No drought conditions 9. Large or Dangerous Stream — assessment reach metric ❑Yes �No Is stream is too large or dangerous to assess? If Yes, skip to Metric 13 (Streamside Area Ground Surface Condition). 10. Natural In-stream Habitat Types — assessment reach metric 10a. ❑Yes �No Degraded in-stream habitat over majority of the assessment reach (examples of stressors include excessive sedimentation, mining, excavation, in-stream hardening [for example, rip-rap], recent dredging, and snagging) (evaluate for Size 4 Coastal Plain streams only, then skip to Metric 12) 10b. Check all that occur (occurs if > 5% coverage of assessment reach) (skip for Size 4 Coastal Plain streams) ❑A Multiple aquatic macrophytes and aquatic mosses m�, ❑F 5% oysters or other natural hard bottoms (include liverworts, lichens, and algal mats) � m ❑G Submerged aquatic vegetation �B Multiple sticks and/or leaf packs and/or emergent g Y ❑H Low-tide refugia (pools) vegetation Y L ❑I Sand bottom ❑C Multiple snags and logs (including lap trees) L@ ❑J 5% vertical bank along the marsh �D 5% undercut banks and/or root mats and/or roots �� ❑K Little or no habitat in banks extend to the normal wetted perimeter ❑E Little or no habitat *********************************REMAINING QUESTIONS ARE NOT APPLICABLE FOR TIDAL MARSH STREAMS**************************** 11. Bedform and Substrate — assessment reach metric (skip for Size 4 Coastal Plain streams and Tidal Marsh Streams) 11a. ❑Yes �No Is assessment reach in a natural sand-bed stream? (skip for Coastal Plain streams) 11 b. Bedform evaluated. Check the appropriate box(es). ❑A Riffle-run section (evaluate 11c) �B Pool-glide section (evaluate 11d) ❑C Natural bedform absent (skip to Metric 12, Aquatic Life) 11 c. In riffle sections, check all that occur below the normal wetted perimeter of the assessment reach — whether or not submerged. Check at least one box in each row (skip for Size 4 Coastal Plain streams and Tidal Marsh Streams). Not Present (NP) = absent, Rare (R) = present but < 10%, Common (C) _> 10-40%, Abundant (A) _> 40-70%, Predominant (P) _> 70%. Cumulative percentages should not exceed 100% for each assessment reach. NP R C A P ❑ ❑ ❑ ❑ ❑ Bedrock/saprolite ❑ ❑ ❑ ❑ ❑ Boulder (256 — 4096 mm) ❑ ❑ ❑ ❑ ❑ Cobble (64 — 256 mm) ❑ ❑ ❑ ❑ ❑ Gravel (2 — 64 mm) ❑ ❑ ❑ ❑ ❑ Sand (.062 — 2 mm) ❑ ❑ ❑ ❑ ❑ SilUclay (< 0.062 mm) ❑ ❑ ❑ ❑ ❑ Detritus ❑ ❑ ❑ ❑ ❑ Artificial (rip-rap, concrete, etc.) 11d. ❑Yes �No Are pools filled with sediment? (skip for Size 4 Coastal Plain streams and Tidal Marsh Streams) 12. Aquatic Life — assessment reach metric (skip for Tidal Marsh Streams) 12a. �Yes ❑No Was an in-stream aquatic life assessment performed as described in the User Manual? If No, select one of the following reasons and skip to Metric 13. ❑No Water ❑Other: 12b. �Yes ❑No Are aquatic organisms present in the assessment reach (look in riffles, pools, then snags)? If Yes, check all that apply. If No, skip to Metric 13. 1 >1 Numbers over columns refer to "individuals" for Size 1 and 2 streams and "taxa" for Size 3 and 4 streams. ❑ ❑Adult frogs ❑ ❑Aquatic reptiles ❑ ❑Aquatic macrophytes and aquatic mosses (include liverworts, lichens, and algal mats) ❑ ❑Beetles ❑ ❑Caddisfly larvae (T) ❑ ❑Asian clam (Corbicula) ❑ �Crustacean (isopod/amphipod/crayfish/shrimp) ❑ ❑Damselfly and dragonfly larvae ❑ ❑Dipterans ❑ ❑Mayfly larvae (E) ❑ ❑Megaloptera (alderFly, fishfly, dobsonfly larvae) ❑ ❑Midges/mosquito larvae ❑ ❑Mosquito fish (Gambusia) or mud minnows (Umbra pygmaea) ❑ ❑Mussels/Clams (not Corbicula) ❑ ❑Other fish ❑ ❑Salamanders/tadpoles ❑ ❑Snails ❑ ❑Stonefly larvae (P) ❑ ❑Tipulid larvae ❑ ❑Worms/leeches 13. Streamside Area Ground Surface Condition — streamside area metric (skip for Tidal Marsh Streams and B valley types) Consider for the Left Bank (LB) and the Right Bank (RB). Consider storage capacity with regard to both overbank flow and upland runoff. LB RB ❑A �A Little or no alteration to water storage capacity over a majority of the streamside area �B ❑B Moderate alteration to water storage capacity over a majority of the streamside area ❑C ❑C Severe alteration to water storage capacity over a majority of the streamside area (examples: ditches, fill, soil compaction, livestock disturbance, buildings, man-made levees, drainage pipes) 14. Streamside Area Water Storage — streamside area metric (skip for Size 1 streams, Tidal Marsh Streams, and B valley types) Consider for the Left Bank (LB) and the Right Bank (RB) of the streamside area. LB RB ❑A ❑A Majority of streamside area with depressions able to pond water >_ 6 inches deep ❑B ❑B Majority of streamside area with depressions able to pond water 3 to 6 inches deep �C �C Majority of streamside area with depressions able to pond water < 3 inches deep 15. Wetland Presence — streamside area metric (skip for Tidal Marsh Streams) Consider for the Left Bank (LB) and the Right Bank (RB). Do not consider wetlands outside of the streamside area or within the normal wetted perimeter of assessment reach. LB RB ❑Y ❑Y Are wetlands present in the streamside area? �N �N 16. Baseflow Contributors — assessment reach metric (skip for Size 4 streams and Tidal Marsh Streams) Check all contributors within the assessment reach or within view of and draining to the assessment reach. ❑A Streams and/or springs Qurisdictional discharges) �B Ponds (include wet detention basins; do not include sediment basins or dry detention basins) ❑C Obstruction passing flow during low-flow periods within the assessment area (beaver dam, leaky dam, bottom-release dam, weir) ❑D Evidence of bank seepage or sweating (iron in water indicates seepage) �E Stream bed or bank soil reduced (dig through deposited sediment if present) ❑F None of the above 17. Baseflow Detractors — assessment area metric (skip for Tidal Marsh Streams) Check all that apply. ❑A Evidence of substantial water withdrawals from the assessment reach (includes areas excavated for pump installation) ❑B Obstruction not passing flow during low-flow periods affecting the assessment reach (ex: watertight dam, sediment deposit) ❑C Urban stream (>_ 24% impervious surface for watershed) ❑D Evidence that the streamside area has been modified resulting in accelerated drainage into the assessment reach ❑E Assessment reach relocated to valley edge �F None of the above 18. Shading — assessment reach metric (skip for Tidal Marsh Streams) Consider aspect. Consider "leaf-on" condition. ❑A Stream shading is appropriate for stream category (may include gaps associated with natural processes) �B Degraded (example: scattered trees) ❑C Stream shading is gone or largely absent 19. Buffer Width — streamside area metric (skip for Tidal Marsh Streams) Consider "vegetated buffer" and "wooded buffer" separately for left bank (LB) and right bank (RB) starting at the top of bank out to the first break. Vegetated Wooded LB RB LB RB ❑A �A ❑A �A >_ 100 feet wide or extends to the edge of the watershed ❑B ❑B ❑B ❑B From 50 to < 100 feet wide �C ❑C �C ❑C From 30 to < 50 feet wide ❑D ❑D ❑D ❑D From 10 to < 30 feet wide ❑E ❑E ❑E ❑E < 10 feet wide or no trees 20. Buffer Structure — streamside area metric (skip for Tidal Marsh Streams) Consider for left bank (LB) and right bank (RB) for Metric 19 ("Vegetated" Buffer Width). LB RB ❑A �A Mature forest ❑B ❑B Non-mature woody vegetation or modified vegetation structure �C ❑C Herbaceous vegetation with or without a strip of trees < 10 feet wide ❑D ❑D Maintained shrubs ❑E ❑E Little or no vegetation 21. Buffer Stressors — streamside area metric (skip for Tidal Marsh Streams) Check all appropriate boxes for left bank (LB) and right bank (RB). Indicate if listed stressor abuts stream (Abuts), does not abut but is within 30 feet of stream (< 30 feet), or is between 30 to 50 feet of stream (30-50 feet). If none of the following stressors occurs on either bank, check here and skip to Metric 22: ❑ Abuts < 30 feet 30-50 feet LB RB LB RB LB RB ❑A ❑A ❑A ❑A ❑A ❑A Row crops ❑B ❑B �B ❑B �B ❑B Maintained turf ❑C ❑C ❑C ❑C ❑C ❑C Pasture (no livestock)/commercial horticulture ❑D ❑D ❑D ❑D ❑D ❑D Pasture (active livestock use) 22. Stem Density — streamside area metric (skip for Tidal Marsh Streams) Consider for left bank (LB) and right bank (RB) for Metric 19 ("Wooded" Buffer Width). LB RB ❑A �A Medium to high stem density �B ❑B Low stem density ❑C ❑C No wooded riparian buffer or predominantly herbaceous species or bare ground 23. Continuity of Vegetated Buffer — streamside area metric (skip for Tidal Marsh Streams) Consider whether vegetated buffer is continuous along stream (parallel). Breaks are areas lacking vegetation > 10 feet wide. LB RB ❑A �A The total length of buffer breaks is < 25 percent. �B ❑B The total length of buffer breaks is between 25 and 50 percent. ❑C ❑C The total length of buffer breaks is > 50 percent. 24. Vegetative Composition — streamside area metric (skip for Tidal Marsh Streams) Evaluate the dominant vegetation within 100 feet of each bank or to the edge of the watershed (whichever comes first) as it contributes to assessment reach habitat. LB RB ❑A �A Vegetation is close to undisturbed in species present and their proportions. Lower strata composed of native species, with non-native invasive species absent or sparse. ❑B ❑B Vegetation indicates disturbance in terms of species diversity or proportions, but is still largely composed of native species. This may include communities of weedy native species that develop after clear-cutting or clearing or communities with non-native invasive species present, but not dominant, over a large portion of the expected strata or communities missing understory but retaining canopy trees. �C ❑C Vegetation is severely disturbed in terms of species diversity or proportions. Mature canopy is absent or communities with non-native invasive species dominant over a large portion of expected strata or communities composed of planted stands of non-characteristic species or communities inappropriately composed of a single species or no vegetation. 25. Conductivity — assessment reach metric (skip for all Coastal Plain streams) 25a. ❑Yes �No Was conductivity measurement recorded? If No, select one of the following reasons. ❑No Water �Other: 25b. Check the box corresponding to the conductivity measurement (units of microsiemens per centimeter). ❑A < 46 ❑B 46 to < 67 ❑C 67 to < 79 ❑D 79 to < 230 ❑E >_ 230 Notes/Sketch: Assessment reach is a small 1 st order stream which receives water from a BMP pond on the south side of Eastern Avenue. Left bank is partially bordered by maintained lawn with a parking lot approximately 30 feet away at one pond. Remaining buffer consists of mature forest. Right bank is buffered by mature forest for the majority of iYs length. Stream Site Name Stream Category Draft NC SAM Stream Rating Sheet Accompanies User Manual Version 2.1 U-5996 Eastern Ave and Old Date of Assessment 4/19/2018 Carriage Rd Pb1 Assessor Name/Organization Sean Murray, VHB Notes of Field Assessment Form (Y/N) Presence of regulatory considerations (Y/N) Additional stream information/supplementary measurements included (Y/N) NC SAM feature type (perennial, intermittent, Tidal Marsh Stream) Function Class Rating Summary (1) Hydrology (2) Baseflow (2) Flood Flow (3) Streamside Area Attenuation (4) Floodplain Access (4) Wooded Riparian Buffer (4) Microtopography (3) Stream Stability (4) Channel Stability (4) Sediment Transport (4) Stream Geomorphology (2) Stream/Intertidal Zone Interaction (2) Longitudinal Tidal Flow (2) Tidal Marsh Stream Stability (3) Tidal Marsh Channel Stability Tidal Marsh Stream Geomorphol (1) Water Quality (2) Baseflow (2) Streamside Area Vegetation (3) Upland Pollutant Filtration (3) Thermoregulation (2) Indicators of Stressors (2) Aquatic Life Tolerance (2) Intertidal Zone Filtration (1) Habitat (2) In-stream Habitat (3) Baseflow (3) Substrate (3) Stream Stability (3) In-stream Habitat (2) Stream-side Habitat (3) Stream-side Habitat (3) Thermoregulation (2) Tidal Marsh In-stream Habitat (3) Flow Restriction (3) Tidal Marsh Stream Stability (4) Tidal Marsh Channel Stability (4) Tidal Marsh Stream Geomorphology (3) Tidal Marsh In-stream Habitat (2) Intertidal Zone Overall YES YES YES Perennial USACE/ All Streams HIGH HIGH HIGH HIGH HIGH MEDIUM NA HIGH HIGH HIGH HIGH NA NA NA NA NA LOW HIGH MEDIUM MEDIUM MEDIUM NO LOW NA HIGH HIGH HIGH HIGH HIGH HIGH HIGH HIGH MEDIUM NA NA NA NA NA NA NA HIGH NCDWR Intermittent �y/ " _ i; ,, -, NC Division of Water Quality -Meihodology for ldemtificaiion of Interrniitent and Perennial Streams and Their Origins v. 4.11 1�TC l)'@VC� Stre� Date: � � � �'� � �, � � Evaluator: � � � � � ,�' �� Total Points: ° Stream is at /east intermittent if>_ 19 oroerennial if>_ 30� Identi#ication Form Version 4.11 A. Geomorphology (Subtotal = (I n } 1a Continuity of channel bed and bank 2. Sinuosity of channel along thaiweg 3. in-channel sfructure: ex. riffle-pool, step-pool, ripple-pool sequence 4. Particie size of stream substrate 5. Active/relict floodpiain 6. Depositional bars or benches 7. Recent alluvial deposits 8. Headcuts 9. Grade control 10. Naturai vailey 11. Second or greater order channei a artificial ditches are not rated; see discussions in manual B. Hydroloqy (subtotal = ;� ) 12. Presence of Baseflow Project/Site: i�j -,-, ' "r � L.atitude � � ;q ( %�) G,%,"r County: .�� �� Longitude:-%/ �( t;� f�)r:;� �� �, � Stream Determination (circ Other Ephemerai Intermittentt:Perennial e.g. QuadName: s��;, 13. Iron oxidizing bacteria 14. Leaf litter 15. Sediment on plants or debris 16. Organic debris lines or piles 17. Soil-based evidence of high water table? C. Biolo (Subtotal = ��) 18. Fibrous roots in streambed 19. Rooted upland plants in streambed 20. Macrobenthos (note diversity and abundance) 21. Aquatic Mollusks 22. Fish 23. Crayfish 24. Amphibians 25. Algae 26. Wetland plants in streambed 'perennial streams may also be identified using other methods. See Notes: � � fi't_ t`' .' ! �`'� , , 1, ., �n�-,�r< <t Sketch: ' �' Absent 0 0 �� � 0 � 0 1.5 0 0 0=0 3 3 0 0 0 ;�-a-;> 0 F, 35 of manual. G�J Weak 1 1 1 1 0.5 0.5 1 2 2 1 0.5 0.5 Q.5 2 2 2 2 2 Yes=3 2 0.5 1 1 1 E 1 1 = 1.5 Other = 0 Strong ,.,3; 3 3 3 3 3 1.5 1.5 3 3 0 1.5 1.5 0 � 3 1.5 1.5 1.5 1.5 NC SAM FIELD ASSESSMENT RESULTS Accompanies User Manual Version 2.1 USACE AID #: NCDWR #: INSTRUCTIONS: Attach a sketch of the assessment area and photographs. Attach a copy of the USGS 7.5-minute topographic quadrangle, and circle the location of the stream reach under evaluation. If multiple stream reaches will be evaluated on the same property, identify and number all reaches on the attached map, and include a separate form for each reach. See the NC SAM User Manual for detailed descriptions and explanations of requested information. Record in the "Notes/Sketch" section if supplementary measurements were performed. See the NC SAM User Manual for examples of additional measurements that may be relevant. NOTE EVIDENCE OF STRESSORS AFFECTING THE ASSESSMENT AREA (do not need to be within the assessment area). PROJECT/SITE INFORMATION: U-5996 Eastern Ave and Old 1. Project name (if any): Carriage Rd 2. Date of evaluation: 4/19/2018 3. ApplicanUowner name: NCDOT 4. Assessor name/organization: Sean Murray, VHB 5. County: Nash 6. Nearest named water body 7. River basin: Tar-Pamlico on USGS 7.5-minute quad: Stony Creek 8. Site coordinates (decimal degrees, at lower end of assessment reach): 35.970589/-77.931728 STREAM INFORMATION: (depth and width can be approximations) 9. Site number (show on attached map): SB 10. Length of assessment reach evaluated (feet): 390 11. Channel depth from bed (in riffle, if present) to top of bank (feet): 2 ❑Unable to assess channel depth. 12. Channel width at top of bank (feet): 4 13. Is assessment reach a swamp steam? ❑Yes ❑No 14. Feature type: �Perennial flow ❑Intermittent flow ❑Tidal Marsh Stream STREAM CATEGORY INFORMATION: 15. NC SAM Zone: ❑ Mountains (M) � Piedmont (P) ❑ Inner Coastal Plain (I) ❑ Outer Coastal Plain (0) 16. Estimated geomorphic �AL��� J �B valley shape (skip for Tidal Marsh Stream): (more sinuous stream, flatter valley slope) (less sinuous stream, steeper valley slope) 17. Watershed size: (skip �Size 1(< 0.1 mi2) ❑Size 2(0.1 to < 0.5 mi2) ❑Size 3(0.5 to < 5 mi2) ❑Size 4(>_ 5 mi2) for Tidal Marsh Stream) ADDITIONAL INFORMATION: 18. Were regulatory considerations evaluated? �Yes ❑No If Yes, check all that apply to the assessment area. ❑Section 10 water ❑Classified Trout Waters ❑Water Supply Watershed (❑I ❑II ❑III ❑IV ❑V) ❑Essential Fish Habitat ❑Primary Nursery Area ❑ High Quality Waters/Outstanding Resource Waters ❑Publicly owned property �NCDWR Riparian buffer rule in effect ❑Nutrient Sensitive Waters ❑Anadromous fish ❑303(d) List ❑CAMA Area of Environmental Concern (AEC) ❑Documented presence of a federal and/or state listed protected species within the assessment area. List species: ❑Designated Critical Habitat (list species) 19. Are additional stream information/suoolementarv measurements included in "Notes/Sketch" section or attached? 6aYes I-lNo 1. Channel Water - assessment reach metric (skip for Size 1 streams and Tidal Marsh Streams) �A Water throughout assessment reach. ❑B No flow, water in pools only. ❑C No water in assessment reach. 2. Evidence of Flow Restriction - assessment reach metric ❑A At least 10% of assessment reach in-stream habitat or riffle-pool sequence is severely affected by a flow restriction or fill to the point of obstructing flow or a channel choked with aquatic macrophytes or ponded water or impoundment on flood or ebb within the assessment reach (examples: undersized or perched culverts, causeways that constrict the channel, tidal gates, debris jams, beaver dams). �B NotA 3. Feature Pattern - assessment reach metric ❑A A majority of the assessment reach has altered pattern (examples: straightening, modification above or below culvert). �B NotA 4. Feature Longitudinal Profile - assessment reach metric ❑A Majority of assessment reach has a substantially altered stream profile (examples: channel down-cutting, existing damming, over widening, active aggradation, dredging, and excavation where appropriate channel profile has not reformed from any of these disturbances). �B NotA 5. Signs of Active Instability - assessment reach metric Consider only current instability, not past events from which the stream has currently recovered. Examples of instability include active bank failure, active channel down-cutting (head-cut), active widening, and artificial hardening (such as concrete, gabion, rip-rap). �A < 10% of channel unstable ❑B 10 to 25% of channel unstable ❑C > 25% of channel unstable 6. Streamside Area Interaction — streamside area metric Consider for the Left Bank (LB) and the Right Bank (RB). LB RB ❑A �A Little or no evidence of conditions that adversely affect reference interaction �B ❑B Moderate evidence of conditions (examples: berms, levees, down-cutting, aggradation, dredging) that adversely affect reference interaction (examples: limited streamside area access, disruption of flood flows through streamside area, leaky or intermittent bulkheads, causeways with floodplain constriction, minor ditching [including mosquito ditching]) ❑C ❑C Extensive evidence of conditions that adversely affect reference interaction (little to no floodplain/intertidal zone access [examples: causeways with floodplain and channel constriction, bulkheads, retaining walls, fill, stream incision, disruption of flood flows through streamside area] or too much floodplain/intertidal zone access [examples: impoundments, intensive mosquito ditching]) or floodplain/intertidal zone unnaturally absent or assessment reach is a man-made feature on an interstream divide Water Quality Stressors — assessment reach/intertidal zone metric Check all that apply. ❑A Discolored water in stream or intertidal zone (milky white, blue, unnatural water discoloration, oil sheen, stream foam) ❑B Excessive sedimentation (burying of stream features or intertidal zone) ❑C Noticeable evidence of pollutant discharges entering the assessment reach and causing a water quality problem ❑D Odor (not including natural sulfide odors) ❑E Current published or collected data indicating degraded water quality in the assessment reach. Cite source in "Notes/Sketch" section. ❑F Livestock with access to stream or intertidal zone ❑G Excessive algae in stream or intertidal zone ❑H Degraded marsh vegetation in the intertidal zone (removal, burning, regular mowing, destruction, etc) ❑I Other: (explain in "Notes/Sketch" section) �J Little to no stressors 8. Recent Weather — watershed metric (skip for Tidal Marsh Streams) For Size 1 or 2 streams, D1 drought or higher is considered a drought; for Size 3 or 4 streams, D2 drought or higher is considered a drought. ❑A Drought conditions and no rainfall or rainfall not exceeding 1 inch within the last 48 hours ❑B Drought conditions and rainfall exceeding 1 inch within the last 48 hours �C No drought conditions 9. Large or Dangerous Stream — assessment reach metric ❑Yes �No Is stream is too large or dangerous to assess? If Yes, skip to Metric 13 (Streamside Area Ground Surface Condition). 10. Natural In-stream Habitat Types — assessment reach metric 10a. ❑Yes �No Degraded in-stream habitat over majority of the assessment reach (examples of stressors include excessive sedimentation, mining, excavation, in-stream hardening [for example, rip-rap], recent dredging, and snagging) (evaluate for Size 4 Coastal Plain streams only, then skip to Metric 12) 10b. Check all that occur (occurs if > 5% coverage of assessment reach) (skip for Size 4 Coastal Plain streams) ❑A Multiple aquatic macrophytes and aquatic mosses m�, ❑F 5% oysters or other natural hard bottoms (include liverworts, lichens, and algal mats) � m ❑G Submerged aquatic vegetation �B Multiple sticks and/or leaf packs and/or emergent g Y ❑H Low-tide refugia (pools) vegetation Y L ❑I Sand bottom ❑C Multiple snags and logs (including lap trees) L@ ❑J 5% vertical bank along the marsh �D 5% undercut banks and/or root mats and/or roots �� ❑K Little or no habitat in banks extend to the normal wetted perimeter ❑E Little or no habitat *********************************REMAINING QUESTIONS ARE NOT APPLICABLE FOR TIDAL MARSH STREAMS**************************** 11. Bedform and Substrate — assessment reach metric (skip for Size 4 Coastal Plain streams and Tidal Marsh Streams) 11a. ❑Yes �No Is assessment reach in a natural sand-bed stream? (skip for Coastal Plain streams) 11 b. Bedform evaluated. Check the appropriate box(es). ❑A Riffle-run section (evaluate 11c) �B Pool-glide section (evaluate 11d) ❑C Natural bedform absent (skip to Metric 12, Aquatic Life) 11 c. In riffle sections, check all that occur below the normal wetted perimeter of the assessment reach — whether or not submerged. Check at least one box in each row (skip for Size 4 Coastal Plain streams and Tidal Marsh Streams). Not Present (NP) = absent, Rare (R) = present but < 10%, Common (C) _> 10-40%, Abundant (A) _> 40-70%, Predominant (P) _> 70%. Cumulative percentages should not exceed 100% for each assessment reach. NP R C A P ❑ ❑ ❑ ❑ ❑ Bedrock/saprolite ❑ ❑ ❑ ❑ ❑ Boulder (256 — 4096 mm) ❑ ❑ ❑ ❑ ❑ Cobble (64 — 256 mm) ❑ ❑ ❑ ❑ ❑ Gravel (2 — 64 mm) ❑ ❑ ❑ ❑ ❑ Sand (.062 — 2 mm) ❑ ❑ ❑ ❑ ❑ SilUclay (< 0.062 mm) ❑ ❑ ❑ ❑ ❑ Detritus ❑ ❑ ❑ ❑ ❑ Artificial (rip-rap, concrete, etc.) 11d. ❑Yes �No Are pools filled with sediment? (skip for Size 4 Coastal Plain streams and Tidal Marsh Streams) 12. Aquatic Life — assessment reach metric (skip for Tidal Marsh Streams) 12a. �Yes ❑No Was an in-stream aquatic life assessment performed as described in the User Manual? If No, select one of the following reasons and skip to Metric 13. ❑No Water ❑Other: 12b. �Yes ❑No Are aquatic organisms present in the assessment reach (look in riffles, pools, then snags)? If Yes, check all that apply. If No, skip to Metric 13. 1 >1 Numbers over columns refer to "individuals" for Size 1 and 2 streams and "taxa" for Size 3 and 4 streams. ❑ ❑Adult frogs ❑ ❑Aquatic reptiles ❑ ❑Aquatic macrophytes and aquatic mosses (include liverworts, lichens, and algal mats) ❑ ❑Beetles ❑ ❑Caddisfly larvae (T) ❑ ❑Asian clam (Corbicula) ❑ �Crustacean (isopod/amphipod/crayfish/shrimp) ❑ ❑Damselfly and dragonfly larvae ❑ ❑Dipterans ❑ �Mayfly larvae (E) ❑ ❑Megaloptera (alderFly, fishfly, dobsonfly larvae) ❑ ❑Midges/mosquito larvae ❑ ❑Mosquito fish (Gambusia) or mud minnows (Umbra pygmaea) ❑ �Mussels/Clams (not Corbicula) ❑ ❑Other fish ❑ ❑Salamanders/tadpoles ❑ ❑Snails ❑ ❑Stonefly larvae (P) ❑ ❑Tipulid larvae ❑ �Worms/leeches 13. Streamside Area Ground Surface Condition — streamside area metric (skip for Tidal Marsh Streams and B valley types) Consider for the Left Bank (LB) and the Right Bank (RB). Consider storage capacity with regard to both overbank flow and upland runoff. LB RB �A �A Little or no alteration to water storage capacity over a majority of the streamside area ❑B ❑B Moderate alteration to water storage capacity over a majority of the streamside area ❑C ❑C Severe alteration to water storage capacity over a majority of the streamside area (examples: ditches, fill, soil compaction, livestock disturbance, buildings, man-made levees, drainage pipes) 14. Streamside Area Water Storage — streamside area metric (skip for Size 1 streams, Tidal Marsh Streams, and B valley types) Consider for the Left Bank (LB) and the Right Bank (RB) of the streamside area. LB RB ❑A ❑A Majority of streamside area with depressions able to pond water >_ 6 inches deep ❑B ❑B Majority of streamside area with depressions able to pond water 3 to 6 inches deep �C �C Majority of streamside area with depressions able to pond water < 3 inches deep 15. Wetland Presence — streamside area metric (skip for Tidal Marsh Streams) Consider for the Left Bank (LB) and the Right Bank (RB). Do not consider wetlands outside of the streamside area or within the normal wetted perimeter of assessment reach. LB RB ❑Y �Y Are wetlands present in the streamside area? �N ❑N 16. Baseflow Contributors — assessment reach metric (skip for Size 4 streams and Tidal Marsh Streams) Check all contributors within the assessment reach or within view of and draining to the assessment reach. �A Streams and/or springs Qurisdictional discharges) �B Ponds (include wet detention basins; do not include sediment basins or dry detention basins) ❑C Obstruction passing flow during low-flow periods within the assessment area (beaver dam, leaky dam, bottom-release dam, weir) �D Evidence of bank seepage or sweating (iron in water indicates seepage) �E Stream bed or bank soil reduced (dig through deposited sediment if present) ❑F None of the above 17. Baseflow Detractors — assessment area metric (skip for Tidal Marsh Streams) Check all that apply. ❑A Evidence of substantial water withdrawals from the assessment reach (includes areas excavated for pump installation) ❑B Obstruction not passing flow during low-flow periods affecting the assessment reach (ex: watertight dam, sediment deposit) ❑C Urban stream (>_ 24% impervious surface for watershed) ❑D Evidence that the streamside area has been modified resulting in accelerated drainage into the assessment reach ❑E Assessment reach relocated to valley edge �F None of the above 18. Shading — assessment reach metric (skip for Tidal Marsh Streams) Consider aspect. Consider "leaf-on" condition. ❑A Stream shading is appropriate for stream category (may include gaps associated with natural processes) �B Degraded (example: scattered trees) ❑C Stream shading is gone or largely absent 19. Buffer Width — streamside area metric (skip for Tidal Marsh Streams) Consider "vegetated buffer" and "wooded buffer" separately for left bank (LB) and right bank (RB) starting at the top of bank out to the first break. Vegetated Wooded LB RB LB RB ❑A ❑A ❑A ❑A >_ 100 feet wide or extends to the edge of the watershed ❑B ❑B ❑B ❑B From 50 to < 100 feet wide ❑C �C ❑C �C From 30 to < 50 feet wide �D ❑D �D ❑D From 10 to < 30 feet wide ❑E ❑E ❑E ❑E < 10 feet wide or no trees 20. Buffer Structure — streamside area metric (skip for Tidal Marsh Streams) Consider for left bank (LB) and right bank (RB) for Metric 19 ("Vegetated" Buffer Width). LB RB ❑A ❑A Mature forest �B �B Non-mature woody vegetation or modified vegetation structure ❑C ❑C Herbaceous vegetation with or without a strip of trees < 10 feet wide ❑D ❑D Maintained shrubs ❑E ❑E Little or no vegetation 21. Buffer Stressors — streamside area metric (skip for Tidal Marsh Streams) Check all appropriate boxes for left bank (LB) and right bank (RB). Indicate if listed stressor abuts stream (Abuts), does not abut but is within 30 feet of stream (< 30 feet), or is between 30 to 50 feet of stream (30-50 feet). If none of the following stressors occurs on either bank, check here and skip to Metric 22: ❑ Abuts < 30 feet 30-50 feet LB RB LB RB LB RB ❑A ❑A ❑A ❑A ❑A ❑A Row crops �B �B �B �B �B �B Maintained turf ❑C ❑C ❑C ❑C ❑C ❑C Pasture (no livestock)/commercial horticulture ❑D ❑D ❑D ❑D ❑D ❑D Pasture (active livestock use) 22. Stem Density — streamside area metric (skip for Tidal Marsh Streams) Consider for left bank (LB) and right bank (RB) for Metric 19 ("Wooded" Buffer Width). LB RB ❑A �A Medium to high stem density �B ❑B Low stem density ❑C ❑C No wooded riparian buffer or predominantly herbaceous species or bare ground 23. Continuity of Vegetated Buffer — streamside area metric (skip for Tidal Marsh Streams) Consider whether vegetated buffer is continuous along stream (parallel). Breaks are areas lacking vegetation > 10 feet wide. LB RB ❑A ❑A The total length of buffer breaks is < 25 percent. �B �B The total length of buffer breaks is between 25 and 50 percent. ❑C ❑C The total length of buffer breaks is > 50 percent. 24. Vegetative Composition — streamside area metric (skip for Tidal Marsh Streams) Evaluate the dominant vegetation within 100 feet of each bank or to the edge of the watershed (whichever comes first) as it contributes to assessment reach habitat. LB RB ❑A ❑A Vegetation is close to undisturbed in species present and their proportions. Lower strata composed of native species, with non-native invasive species absent or sparse. �B �B Vegetation indicates disturbance in terms of species diversity or proportions, but is still largely composed of native species. This may include communities of weedy native species that develop after clear-cutting or clearing or communities with non-native invasive species present, but not dominant, over a large portion of the expected strata or communities missing understory but retaining canopy trees. ❑C ❑C Vegetation is severely disturbed in terms of species diversity or proportions. Mature canopy is absent or communities with non-native invasive species dominant over a large portion of expected strata or communities composed of planted stands of non-characteristic species or communities inappropriately composed of a single species or no vegetation. 25. Conductivity — assessment reach metric (skip for all Coastal Plain streams) 25a. ❑Yes �No Was conductivity measurement recorded? If No, select one of the following reasons. ❑No Water �Other: 25b. Check the box corresponding to the conductivity measurement (units of microsiemens per centimeter). ❑A < 46 ❑B 46 to < 67 ❑C 67 to < 79 ❑D 79 to < 230 ❑E >_ 230 Notes/Sketch: Assessment reach is a small stream which flows into Stony Creek to the north. It crosses Eastern Avenue through a culvert. South of Eastern Ave the buffer is upland and has been cleared leaving scattered trees, maintained lawn, and virtually no midstory/shrub stratum. North of the road, the stream is buffered by hardwood wetland on the right bank and upland forest on the left bank. Most of this area appears relatively undisturbed. Stream Site Name Stream Category Draft NC SAM Stream Rating Sheet Accompanies User Manual Version 2.1 U-5996 Eastern Ave and Old Date of Assessment 4/19/2018 Carriage Rd Pb1 Assessor Name/Organization Sean Murray, VHB Notes of Field Assessment Form (Y/N) Presence of regulatory considerations (Y/N) Additional stream information/supplementary measurements included (Y/N) NC SAM feature type (perennial, intermittent, Tidal Marsh Stream) Function Class Rating Summary (1) Hydrology (2) Baseflow (2) Flood Flow (3) Streamside Area Attenuation (4) Floodplain Access (4) Wooded Riparian Buffer (4) Microtopography (3) Stream Stability (4) Channel Stability (4) Sediment Transport (4) Stream Geomorphology (2) Stream/Intertidal Zone Interaction (2) Longitudinal Tidal Flow (2) Tidal Marsh Stream Stability (3) Tidal Marsh Channel Stability Tidal Marsh Stream Geomorphol (1) Water Quality (2) Baseflow (2) Streamside Area Vegetation (3) Upland Pollutant Filtration (3) Thermoregulation (2) Indicators of Stressors (2) Aquatic Life Tolerance (2) Intertidal Zone Filtration (1) Habitat (2) In-stream Habitat (3) Baseflow (3) Substrate (3) Stream Stability (3) In-stream Habitat (2) Stream-side Habitat (3) Stream-side Habitat (3) Thermoregulation (2) Tidal Marsh In-stream Habitat (3) Flow Restriction (3) Tidal Marsh Stream Stability (4) Tidal Marsh Channel Stability (4) Tidal Marsh Stream Geomorphology (3) Tidal Marsh In-stream Habitat (2) Intertidal Zone Overall YES YES YES Perennial USACE/ All Streams HIGH HIGH HIGH HIGH HIGH MEDIUM NA HIGH HIGH HIGH HIGH NA NA NA NA NA HIGH HIGH LOW LOW MEDIUM NO HIGH NA HIGH HIGH HIGH HIGH HIGH HIGH MEDIUM MEDIUM MEDIUM NA NA NA NA NA NA NA HIGH NCDWR Intermittent `�h� WETLAND DETERMINATION DATA FORM - Eastern Mountains and Piedmont Region DP-Wl4-1 Project Site: Old Carriage Road and Eastern Avenue City/County: Rocky Mount Samp. Date: 1/30/2018 Applicant/Owner: NCDOT State: NC Sampling Point: DP-WA-1 Investigator(s): C. Robertson Section, Township, Range: Landform(n�nSioPe,cerra�e,ec�.): Terrace Localrelief(concave,convex,none): �oncave Slope(%): Sto10 Subregion (LRR or MLRA): LRR P MLRA 133A Lat: 35.971106 Long: -7737314 Datum: WG584 Soil Map Unit: Bibb loam, 0-2%slopes NWI Classif.: PFO3A Are climatic/hydrologic conditions on the site typical for this time of year? Yes (If no, explain in Remarks.) Are Vegetation, Soil, or Hydrology significantly disturbed? No Normal Circumstances? Yes Are Vegetation, Soil, or Hydrology naturally problematic? No (If needed, explain any answers in Remarks.) SUMMARY OF FINDINGS - Attach site Hydrophytic Vegetation Present? YES Hydric Soil Present? YES Wetland Hydrology Present? YES HYDROLOGY Primarv Indicators nt locations, transects, important features, etc. All parameters are met. Area is classified as a palustrine forested ( Data point located approximately 40 ft west of wetland flag WA-2 of one is required; check all that a Surface Water (A1) High Water Table (A2) Saturetion (A3) Water Marks (Bl) Sediment Deposits (82) Drift Deposits (83) Algal Mat or Crust (B4) Iron Deposits (BS) Inundation Visible on Aerial (87) Water-Stained Leaves (69) Aquatic Fauna (813) True Aquatic Plants (614) Hydrogen Sulfide Odor (C1) X Oxidized Rhizospheres on Living Roots (C3) Presence of Reduced Iron (C4) Recent Iron Reduction in Tilled Soils (C6) Thin Muck Surface (C7) Other (Explain in Remarks) Is This Sample Area Within a Wetland? YES icators (minimum of two Sparsely Vegetated Concave Surface (B8) X Drainage Patterns (B10) Moss Trim Lines (B16) Dry-Season Water Table (Q) Creyfish Burrows (C8) Saturation Visible on Aerial Imagery (C9) Stunted or Stressed Plants (D1) Geomorphic Position (D2) Microtopogrephic Relief (D4) X FAC-NeutralTest(DS) Surface Water Present? yE$ Depth (inches): 2 Water Table Present? YES Depth (inches): surface Wetland Hydrology Present? Saturation Present? YES Depth (inches): surfate Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: NA one primary indicator or two 501 L present; parameter is met. YES Profile Description: Describe to the depth needed to document the indicator or confirm the absence of indicators. Depth Matrix Redox Features (in) Color (moist) % Color (moist) % Typel LocZ Texture Remarks 0-17 10YR 3 2 90 7.SYR 5 8 10 C M fine sandy loam - �� —� � —IV� c ay oam 'Type: C=Concentration, D=Depletion, RM=Reduced Matrix, MS=Masked Sand Grains. �Location: PL=Pore Lining, M=Matrix. Hydric Soil Indicators: Indicators for Problematic Hydric Soils3: Histosol (Al) Dark Surface (S7) 2 cm Muck (A10) Histic Epipedon (A2) Polyvalue Below Surface (58) CoaSt Prairie Redox (A16) Black Histic (A3) Thin Dark Surface (59) Piedmont Floodplain Soils (F19) Hydrogen Sulfide (A4) Loamy Gleyed Matrix (F2) Very Shallow Dark Surface (TF12) Stratified Layers (AS) Depleted Matrix (F3) Other (Explain in Remarks) 2cm Muck (A10) X Redox Dark Surface (F6) Depleted Below Dark Surface (A11) Depleted Dark Surface (F7) Thick Dark Surface (Al2) Redox Depressions (FS) 3lndicators of hydrophytic vegetation and Sandy Mucky Minerel (51) Iron-Manganese Masses (F12) wetland hydrology must be present, unless Sandy Gleyed Matrix (S4) Umbric Surface (F13) disturbed or problematic. Sandy Redox (55) Piedmont Floodplain Soils (F19) Stripped Matrix (S6) Red Parent Material (F21) Restrictive Layer (if observed): Type: ryq Hydric Soil Present? YES Depth (inches): Remarks: Indicator F6 (Redox Dark Surface) present and soil meets NTCHS definition of hydric soil; parameter is met. Eastern Mountains and Piedmont Region - Version 2.0 (Adapted By: DouglasA. DeBerry, PhD, PWS, PWD) VEGETATION - Use scientific names of plants. Tree Stratum (Plot size: 30' radius ) 1. Liquidambar styraciflua 2. Acer rubrum 3. Ulmus americana 4. 5. 6. 7. Sapling Stratum (Plot size: 30' radius ) 1. 2. 3. 4. 5. 6. 7. Shrub Stratum (Plot size: 15' radius ) 1. Acer rubrum 2. Asimina triloba 3. Ligustrum sinense 4. 5. 6. 7. Herb Stratum (Plot size: 10' radius ) 1. Onoclea sensibilis 2. Carex lupulina 3. Sambucus nigra 4. S. 6. 7. 8. 9. 10. 11. 12. Woody Vines (Plot size: 30' radius ) 1. 2. 3. 4. 5. �� Sampling Point: DP-WA-1 %Cover Sp? Status DominanceTestWorksheet: 63 X FAC # Dominants OBL, FACW, FAC: 3 (A) 15 FAC 15 FACW # Dominants across all strata: 3 (B) % Dominants OBL, FACW, FAC: 100% (A/B) Prevalencelndex Worksheet: 93 = Total Cover Total % Cover of: Multiply By: OBL 3 x 1= 3 FACW 30 x 2= 60 FAC 151 x 3= 453 FACU 15 x 4= 60 UPL x5= Sum: 199 (A) 576 (B) Prevalence Index = B/A = 2.89 = Total Cover Hydrophytic Vegetation Indicators: X Dominance Test is > 50% 55 X FAC X Prevalence Index is <= 3.0 15 FAC Problematic Hydrophytic Vegetationl �e,Pia��� 15 FACU Rapid Test for Hydrophytic Vegetation Morphological Adaptations 'Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Definitions of Vegetation Strata: 85 = TotalCover Tf2e - Woody plants, excluding woody vines, approximately 20ft (6m) or 1$ X FACW more in height and 3in (7.6cm) or larger in diameter at breast height (DBH). 3 OBL 3 FAC $BP�IIIg - Woody plants, excluding woody vines, approximately 20ft (6m) or more in height and less than 3in (7.6cm) DBH. $hfUb - Woody plants, excluding woody vines, approximately 3 to 20ft (1 to 6m) in height. H21'b - All herbaceous (non-woody) plants, including herbaceous vines, regardless of size. Includes woody plants, except woody vines, less than approximately 3ft (lm) in height. 21 = Total Cover WOOdy VIf12 - All woody vines, regardless of height. Hydrophytic Vegetation = TotalCover Present? YES Remarks: (If observed, list morphological adaptations below). Indicator 2(Dominance Test) present with >50� of dominant species across all vegetation strata FAC or wetter. Eastern Mountains and Piedmont Region - Version 2.0 (Adapted By: DouglasA. DeBerry, PhD, PWS, PWD) �h� WETLAND DETERMINATION DATA FORM - Eastern Mountains and Piedmont Region DP_WA_2 Project Site: Old Carriage Road and Eastern Avenue City/County: Rocky Mount Samp. Date: 1/30/2018 Applicant/Owner: NCDOT State: NC Sampling Point: DP-WA-2 Investigator(s): C. Robertson Section, Township, Range: Landfofm(hillslope,terrace,etc.): HIIISIOp2 Localrelief(concave,convex,none): COIlV2X Slope(%): St010 Subregion (LRR or MLRA): LRR P MLRA 133A Lat: 35.970998 Long: -7737314 Datum: WG584 Soil Map Unit: Gritney sandy loam, 6-30%slopes NWI Classif.: PFO3A Are climatic/hydrologic conditions on the site typical for this time of year? Yes (If no, explain in Remarks.) Are Vegetation, Soil, or Hydrology significantly disturbed? No Normal Circumstances? Yes Are Vegetation, Soil, or Hydrology naturally problematic? No (If needed, explain any answers in Remarks.) SUMMARY OF FINDINGS - Attach site Hydrophytic Vegetation Present? NO Hydric Soil Present? NO Wetland Hydrology Present? NO HYDROLOGY Primarv Indicators nt locations, transects, important features, etc. One or more parameters lacking. Area is not a wetland. Data point located 40 ft east and 20 ft south wetland flag WA-4. of one is required; check all that a Surface Water (A1) High Water Table (A2) Saturetion (A3) Water Marks (Bl) Sediment Deposits (82) Drift Deposits (83) Algal Mat or Crust (B4) Iron Deposits (BS) Inundation Visible on Aerial (87) Water-Stained Leaves (89) Aquatic Fauna (813) True Aquatic Plants (614) Hydrogen Sulfide Odor (C1) Oxidized Rhizospheres on Living Roots (C3) Presence of Reduced Iron (C4) Recent Iron Reduction in Tilled Soils (C6) Thin Muck Surface (C7) Other (Explain in Remarks) Is This Sample Area Within a Wetland? NO icators (minimum of two Sparsely Vegetated Concave Surface (B8) Drainage Patterns (B10) Moss Trim Lines (B16) Dry-Season Water Table (Q) Creyfish Burrows (C8) Saturation Visible on Aerial Imagery (C9) Stunted or Stressed Plants (D1) Geomorphic Position (D2) Microtopographic Relief (D4) FAC-NeutralTest(DS) Surface Water Present? Np Depth (inches): NA Water Table Present? NO Depth (inches): >18 Wetland Hydrology Present? Saturation Present? ryp Depth (inches): �18 Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: NA ry or 501 L present; parameter is not met. NO Profile Description: Describe to the depth needed to document the indicator or confirm the absence of indicators. Depth Matrix Redox Features (in) Color (moist) % Color (moist) % Typel LocZ Texture Remarks 0-20 10YR 5 8 300 sandy loam 'Type: C=Concentration, D=Depletion, RM=Reduced Matrix, MS=Masked Sand Grains. �Location: PL=Pore Lining, M=Matrix. Hydric Soil Indicators: Indicators for Problematic Hydric Soils3: Histosol (Al) Dark Surface (S7) 2 cm Muck (A10) Histic Epipedon (A2) Polyvalue Below Surface (58) CoaSt Prairie Redox (A16) Black Histic (A3) Thin Dark Surface (59) Piedmont Floodplain Soils (F19) Hydrogen Sulfide (A4) Loamy Gleyed Matrix (F2) Very Shallow Dark Surface (TF12) Stratified Layers (AS) Depleted Matrix (F3) Other (Explain in Remarks) 2cm Muck (A10) Redox Dark Surface (F6) Depleted Below Dark Surface (A11) Depleted Dark Surface (F7) Thick Dark Surface (Al2) Redox Depressions (FS) 3lndicators of hydrophytic vegetation and Sandy Mucky Minerel (51) Iron-Manganese Masses (F12) wetland hydrology must be present, unless Sandy Gleyed Matrix (S4) Umbric Surface (F13) disturbed or problematic. Sandy Redox (55) Piedmont Floodplain Soils (F19) Stripped Matrix (S6) Red Parent Material (F21) Restrictive Layer (if observed): Type: ryq Hydric Soil Present? NO Depth (inches): Remarks: No hydric soil indicators present and soil does not meet NTCHS definition of hydric soil; parameter is not met. Eastern Mountains and Piedmont Region - Version 2.0 (Adapted By: DouglasA. DeBerry, PhD, PWS, PWD) VEGETATION - Use scientific names of plants. Tree Stratum (Plot size: 30' radius ) 1. Liquidambar styraciflua 2. Quercus rubra 3. Acer rubrum 4. 5. 6. 7. Sapling Stratum (Plot size: 30' radius ) 1. 2. 3. 4. 5. 6. 7. Shrub Stratum (Plot size: 15' radius ) 1. Liriodendron tulipifera 2. Carpinus caroliniana 3. Fagus grandifolia 4. Ligustrum sinense 5. Quercus rubra 6. 7. Herb Stratum (Plot size: 10' radius ) 1. Polystichum acrostichoides 2. Hedera helix 3. Lonicera japonica 4. Campsis radicans 5. Toxicodendron radicans 6. Sambucus nigra 7. 8. 9. 10. 11. 12. Woody Vines (Plot size: 30' radius ) 1. 2. 3. 4. 5. % Cover Sp? Status 63 X FAC 15 FACU 3 FAC 81 15 15 15 15 3 63 15 15 3 3 3 3 �� Sampling Point: DP-WA-2 Dominance Test Worksheet: # Dominants OBL, FACW, FAC: # Dominants across all strata: % Dominants OBL, FACW, FAC: Prevalencelndex Worksheet: 2 (A) 7 (B) 29� (A/B) = Total Cover Total % Cover of: Multiply By: OBL x 1 = FACW x 2 = FAC 90 x 3= 270 FACU 96 x 4= 384 UPL x5= Sum: 186 (A) 654 (B) Prevalence Index = B/A = 3.52 = Total Cover Hydrophytic Vegetation Indicators: Dominance Test is > 50% X FACU Prevalence Index is <= 3.0 X FAC Problematic Hydrophytic Vegetationl �e,Pia��� X FACU Rapid Test for Hydrophytic Vegetation X FACU Morphological Adaptations FACU 'Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Definitions of Vegetation Strata: = TotalCover Tf2e - Woody plants, excluding woody vines, approximately 20ft (6m) or X FACU more in height and 3in (7.6cm) or larger in diameter at breast height (DBH). X FACU FACU FAC SBPIIIIg-Woodyplants,excludingwoodyvines,approximately20ft(6m) FAC or more in height and less than 3in (7.6cm) DBH. FAC 42 = TotalCover = TotalCover Remarks: (If observed, list morphological adaptations below). No hydrophytic vegetation indicators present; parameter is not met. $hfUb - Woody plants, excluding woody vines, approximately 3 to 20ft (1 to 6m) in height. H21'b - All herbaceous (non-woody) plants, including herbaceous vines, regardless of size. Includes woody plants, except woody vines, less than approximately 3ft (lm) in height. WOOdy VIf12 - All woody vines, regardless of height. Hydrophytic Vegetation Present? NO Eastern Mountains and Piedmont Region - Version 2.0 (Adapted By: DouglasA. DeBerry, PhD, PWS, PWD) �h� WETLAND DETERMINATION DATA FORM - Eastern Mountains and Piedmont Region DP-WB-1 Project Site: Old Carriage Road and Eastern Avenue City/County: Rocky Mount Samp. Date: 1/30/2018 Applicant/Owner: NCDOT State: NC Sampling Point: DP-WB-1 Investigator(s): 1. Thompson Section, Township, Range: Landform (hinsioPe, terrace, ecc.): Floodplain Local relief (concave, convex, none): �oncave Slope (%): O to 2 Subregion (LRR or MLRA): LRR P MLRA 133A Lat: 35.98869 Long: -7737314 Datum: WG584 Soil Map Unit: Meggett loam, 0-2%slopes NWI Classif.: RSUBH Are climatic/hydrologic conditions on the site typical for this time of year? Yes (If no, explain in Remarks.) Are Vegetation, Soil, or Hydrology significantly disturbed? No Normal Circumstances? Yes Are Vegetation, Soil, or Hydrology naturally problematic? No (If needed, explain any answers in Remarks.) SUMMARY OF FINDINGS - Attach site map sho Hydrophytic Vegetation Present? YES Hydric Soil Present? YES Wetland Hydrology Present? YES HYDROLOGY nt locations, transects, important features, etc. Is This Sample Area Within a Wetland? YES All parameters are met. Area is classified as a palustrine forested (PFO) wetland. Data point located on the north floodplain of Stoney Creek, just west of the bridge. Wetland WC is the same system and this data point is representative of conditions in WC. Primary Indicators (minimum of one is required; check all that a Surface Water (A1) High Water Table (A2) Saturation (A3) Water Marks (Bl) Sediment Deposits (82) Drift Deposits (83) Algal Mat or Crust (64) Iron Deposits (BS) Inundation Visible on Aerial (B7) Water-Stained Leaves (69) Aquatic Fauna (813) True Aquatic Plants (614) Hydrogen Sulfide Odor (C1) X Oxidized Rhizospheres on Living Roots (C3) Presence of Reduced Iron (C4) Recent Iron Reduction in Tilled Soils (C6) Thin Muck Surface (C7) Other (Explain in Remarks) icators (minimum of two Sparsely Vegetated Concave Surface (B8) X Drainage Patterns(B10) Moss Trim Lines (616) Dry-Season Water Table (Q) Crayfish Burrows (C8) Saturation Visible on Aerial Imagery (C9) Stunted or Stressed Plants (D1) X Geomorphic Position (D2) Microtopogrephic Relief (D4) FAC-Neutral Test (DS) Surface Water Present? Np Depth (inches): NA Water Table Present? NO Depth (inches): 10 Wetland Hydrology Present? Saturation Present? YES Depth (inches): 6 Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: NA one primary indicator or two 501 L present; parameter is met. YES Profile Description: Describe to the depth needed to document the indicator or confirm the absence of indicators. Depth Matrix Redox Features (in) Color (moist) % Color (moist) % Typel LocZ Texture Remarks 0-6 10YR 4 2 300 loam - �� �� � �� c ay oam 'Type: C=Concentration, D=Depletion, RM=Reduced Matrix, MS=Masked Sand Grains. �Location: PL=Pore Lining, M=Matrix. Hydric Soil Indicators: Indicators for Problematic Hydric Soils3: Histosol (Al) Dark Surface (S7) 2 cm Muck (A10) Histic Epipedon (A2) Polyvalue Below Surface (58) CoaSt PI'ail'ie Redox (A16) Black Histic (A3) Thin Dark Surface (59) Piedmont Floodplain Soils (F19) Hydrogen Sulfide (A4) Loamy Gleyed Matrix (F2) Very Shallow Dark Surface (TF12) Stratified Layers (AS) X Depleted Matrix (F3) Other (Explain in Remarks) 2cm Muck (A10) Redox Dark Surface (F6) Depleted Below Dark Surface (A11) Depleted Dark Surface (F7) Thick Dark Surface (Al2) Redox Depressions (F8) 3lndicators of hydrophytic vegetation and Sandy Mucky Minerel (51) Iron-Manganese Masses (F12) wetland hydrology must be present, unless Sandy Gleyed Matrix (54) Umbric Surface (F13) disturbed or problematic. Sandy Redox (SS) Piedmont Floodplain Soils (F19) Stripped Matrix (56) Red Parent Material (F21) Restrictive Layer (if observed): Type: ryq Hydric Soil Present? YES Depth (inches): Remarks: Indicator F3 (Depleted Matrix) present and soil meets NTCHS definition of hydric soil; parameter is met. Eastern Mountains and Piedmont Region - Version 2.0 (Adapted By: Douglas A. DeBerry, PhD, PWS, PWD) VEGETATION - Use scientific names of plants. Tree Stratum (Plot size: 30' radius ) 1. Quercus phellos 2. Liquidambar styraciflua 3. Acer rubrum 4. Betula nigra 5. Fraxinus pennsylvanica 6. 7. Sapling Stratum (Plot size: 30' radius ) 1. 2. 3. 4. 5. 6. 7. Shrub Stratum (Plot size: 15' radius ) 1. Carpinus caroliniana 2. Viburnum prunifolium 3. 4. 5. 6. 7. Herb Stratum (Plot size: 10' radius ) 1. Chasmanthium latifolium 2. Carex crinita 3. Viola sororia 4. S. 6. 7. 8. 9. 10. 11. 12. Woody Vines (Plot size: 30' radius ) 1. 2. 3. 4. 5. �� Sampling Point: DP-WB-1 %Cover Sp? Status DominanceTestWorksheet: 63 X FAC # Dominants OBL, FACW, FAC: 3 (A) 63 X FAC 15 FAC # Dominants across all strata: 5 (B) 15 FACW 3 FACW % Dominants OBL, FACW, FAC: 60% (A/B) Prevalencelndex Worksheet: 159 = Total Cover Total % Cover of: Multiply By: OBL 3 x 1= 3 FACW 18 x 2= 36 FAC 147 x 3= 441 FACU 41 x 4= 164 UPL x5= Sum: 209 (A) 644 (B) Prevalence Index = B/A = 3.08 = Total Cover Hydrophytic Vegetation Indicators: X Dominance Test is > 50% 3 X FAC Prevalence Index is <= 3.0 3 X FACU Problematic Hydrophytic Vegetationl �e,Pia��� Rapid Test for Hydrophytic Vegetation Morphological Adaptations 'Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Definitions of Vegetation Strata: 6 = Total Cover Tf2e - Woody plants, excluding woody vines, approximately 20k (6m) or 3$ X FACU more in height and 3in (7.6cm) or larger in diameter at breast height (DBH). 3 OBL 3 FAC $BP�IfIg - Woody plants, excluding woody vines, approximately 20ft (6m) or more in height and less than 3in (7.6cm) DBH. $hfUb - Woody plants, excluding woody vines, approximately 3 to 20k (1 to 6m) in height. H21'b - All herbaceous (non-woody) plants, including herbaceous vines, regardless of size. Includes woody plants, except woody vines, less than approximately 3ft (1m) in height. 44 = Total Cover WOOdy VIf12 - All woody vines, regardless of height. Hydrophytic Vegetation = TotalCover Present? YES Remarks: (If observed, list morphological adaptations below). Indicator 2(Dominance Test) present with >50� of dominant species across all vegetation strata FAC or wetter. Eastern Mountains and Piedmont Region - Version 2.0 (Adapted By: Douglas A. DeBerry, PhD, PWS, PWD) `�h� WETLAND DETERMINATION DATA FORM - Eastern Mountains and Piedmont Region DP_WB_2 Project Site: Old Carriage Road and Eastern Avenue City/County: Rocky Mount Samp. Date: 1/30/2018 Applicant/Owner: NCDOT State: NC Sampling Point: DP-WB-2 Investigator(s): 1. Thompson Section, Township, Range: Landform (n�nSioPe, cerra�e, ec�.): Terrace Local relief (concave, convex, none): �onvex Slope (%): O to 2 Subregion (LRR or MLRA): LRR P MLRA 133A Lat: 35.988916 Long: -7737314 Datum: WG584 Soil Map Unit: Meggett loam, 0-2%slopes NWI Classif.: None Are climatic/hydrologic conditions on the site typical for this time of year? Yes (If no, explain in Remarks.) Are Vegetation, Soil, or Hydrology significantly disturbed? No Normal Circumstances? Yes Are Vegetation, Soil, or Hydrology naturally problematic? No (If needed, explain any answers in Remarks.) SUMMARY OF FINDINGS - Attach site map sho Hydrophytic Vegetation Present? YES Hydric Soil Present? YES Wetland Hydrology Present? NO One or more parameters lacking. Area is not a w Data point located north of data point DP-WB-1. HYDROLOGY Primary Indicators (minimum of one is required; check all that a Surface Water (A1) High Water Table (A2) Saturation (A3) Water Marks (Bl) Sediment Deposits (82) Drift Deposits (83) Algal Mat or Crust (64) Iron Deposits (BS) Inundation Visible on Aerial (B7) Water-Stained Leaves (69) nt locations, transects, important features, etc. Aquatic Fauna (813) True Aquatic Plants (614) Hydrogen Sulfide Odor (C1) Oxidized Rhizospheres on Living Roots (C3) Presence of Reduced Iron (C4) Recent Iron Reduction in Tilled Soils (C6) Thin Muck Surface (C7) Other (Explain in Remarks) Is This Sample Area Within a Wetland? NO icators (minimum of two Sparsely Vegetated Concave Surface (B8) Drainage Patterns (B10) Moss Trim Lines (616) Dry-Season Water Table (Q) Crayfish Burrows (C8) Saturation Visible on Aerial Imagery (C9) Stunted or Stressed Plants (D1) Geomorphic Position (D2) Microtopogrephic Relief (D4) FAC-Neutral Test (DS) Surface Water Present? Np Depth (inches): NA Water Table Present? NO Depth (inches): >18 Wetland Hydrology Present? Saturation Present? ryp Depth (inches): �18 Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: NA ry or 501 L present; parameter is not met. NO Profile Description: Describe to the depth needed to document the indicator or confirm the absence of indicators. Depth Matrix Redox Features (in) Color (moist) % Color (moist) % Typel LocZ Texture Remarks 0-18 10YR 5 2 80 10YR 5 8 10 C M clay ���-� 'Type: C=Concentration, D=Depletion, RM=Reduced Matrix, MS=Masked Sand Grains. �Location: PL=Pore Lining, M=Matrix. Hydric Soil Indicators: Indicators for Problematic Hydric Soils3: Histosol (Al) Dark Surface (S7) 2 cm Muck (A10) Histic Epipedon (A2) Polyvalue Below Surface (58) CoaSt PI'ail'ie Redox (A16) Black Histic (A3) Thin Dark Surface (59) Piedmont Floodplain Soils (F19) Hydrogen Sulfide (A4) Loamy Gleyed Matrix (F2) Very Shallow Dark Surface (TF12) Stratified Layers (AS) X Depleted Matrix (F3) Other (Explain in Remarks) 2cm Muck (A10) Redox Dark Surface (F6) Depleted Below Dark Surface (A11) Depleted Dark Surface (F7) Thick Dark Surface (Al2) Redox Depressions (F8) 3lndicators of hydrophytic vegetation and Sandy Mucky Minerel (51) Iron-Manganese Masses (F12) wetland hydrology must be present, unless Sandy Gleyed Matrix (54) Umbric Surface (F13) disturbed or problematic. Sandy Redox (SS) Piedmont Floodplain Soils (F19) Stripped Matrix (56) Red Parent Material (F21) Restrictive Layer (if observed): Type: ryq Hydric Soil Present? YES Depth (inches): Remarks: Indicator F3 (Depleted Matrix) present and soil meets NTCHS definition of hydric soil; parameter is met. Soil may be a relic floodplain soil, no apparent A or O horizon. Likely disturbed from recent construction. Eastern Mountains and Piedmont Region - Version 2.0 (Adapted By: Douglas A. DeBerry, PhD, PWS, PWD) VEGETATION - Use scientific names of plants. Tree Stratum (Plot size: 30' radius ) 1. Fraxinus pennsylvanica 2. 3. 4. 5. 6. 7. Sapling Stratum (Plot size: 30' radius ) 1. 2. 3. 4. 5. 6. 7. Shrub Stratum (Plot size: 15' radius ) 1. Acer rubrum 2. Ligustrum sinense 3. Liquidambar styraciflua 4. 5. 6. 7. Herb Stratum (Plot size: 10' radius ) 1. Rubus pensilvanicus 2. Lonicera japonica 3. Solidago rugosa 4. Andropogon virginicus 5. Glechoma hederacea 6. Microstegium vimineum 7. 8. 9. 10. 11. 12. Woody Vines (Plot size: 30' radius ) 1. 2. 3. 4. 5. �� Sampling Point: DP-WB-2 %Cover Sp? Status DominanceTestWorksheet: 38 X FACW # Dominants OBL, FACW, FAC: 3 (A) # Dominants across all strata: 5 (B) % Dominants OBL, FACW, FAC: 60% (A/B) Prevalencelndex Worksheet: 38 = Total Cover Total % Cover of: Multiply By: OBL x 1 = FACW 38 x 2= 76 FAC 134 x 3= 402 FACU 106 x 4= 424 UPL x5= Sum: 278 (A) 902 (B) Prevalence Index = B/A = 3.24 = Total Cover Hydrophytic Vegetation Indicators: X Dominance Test is > 50% 38 X FAC Prevalence Index is <= 3.0 38 X FACU Problematic Hydrophytic Vegetationl �e,Pia��� 3 FAC Rapid Test for Hydrophytic Vegetation Morphological Adaptations 'Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Definitions of Vegetation Strata: 79 = Total Cover Tf2e - Woody plants, excluding woody vines, approximately 20k (6m) or 63 X FAC more in height and 3in (7.6cm) or larger in diameter at breast height (DBH). 38 X FACU 15 FAC 15 FACU SBPIIfIg - Woody plants, excluding woody vines, approximately 20ft (6m) 15 FACU or more in height and less than 3in (7.6cm) DBH. 15 FAC $hfUb - Woody plants, excluding woody vines, approximately 3 to 20k (1 to 6m) in height. H21'b - All herbaceous (non-woody) plants, including herbaceous vines, regardless of size. Includes woody plants, except woody vines, less than approximately 3ft (1m) in height. 161 = Total Cover WOOdy VIf12 - All woody vines, regardless of height. Hydrophytic Vegetation = TotalCover Present? YES Remarks: (If observed, list morphological adaptations below). Indicator 2(Dominance Test) present with >50� of dominant species across all vegetation strata FAC or wetter. Eastern Mountains and Piedmont Region - Version 2.0 (Adapted By: Douglas A. DeBerry, PhD, PWS, PWD) �h� WETLAND DETERMINATION DATA FORM - Eastern Mountains and Piedmont Region DP-WD-1 Project Site: Old Carriage Road and Eastern Avenue City/County: Rocky Mount Samp. Date: 1/30/2018 Applicant/Owner: NCDOT State: NC Sampling Point: DP-WD-1 Investigator(s): 1. Thompson Section, Township, Range: Landform (n�nSioPe,cerra�e,ec�.): Bottomland Swamp Local relief (concave,convex, none): �oncave Slope (%): Oto 2 Subregion (LRR or MLRA): LRR P MLRA 133A Lat: 35.989693 Long: -7737314 Datum: WG584 Soil Map Unit: Meggett loam, 0-2%slopes NWI Classif.: PF01C Are climatic/hydrologic conditions on the site typical for this time of year? Yes (If no, explain in Remarks.) Are Vegetation, Soil, or Hydrology significantly disturbed? No Normal Circumstances? Yes Are Vegetation, Soil, or Hydrology naturally problematic? No (If needed, explain any answers in Remarks.) SUMMARY OF FINDINGS - Attach site Hydrophytic Vegetation Present? YES Hydric Soil Present? YES Wetland Hydrology Present? YES HYDROLOGY Primarv Indicators nt locations, transects, important features, etc. All parameters are met. Area is classified as a palustrine for Data point located about 40 ft west of wetland flag WD-17. of one is required; check all that a Surface Water (A1) High Water Table (A2) Saturetion (A3) Water Marks (Bl) Sediment Deposits (82) Drift Deposits (63) Algal Mat or Crust (B4) Iron Deposits (BS) Inundation Visible on Aerial (87) Water-Stained Leaves (89) Aquatic Fauna (813) True Aquatic Plants (614) Hydrogen Sulfide Odor (C1) Oxidized Rhizospheres on Living Roots (C3) Presence of Reduced Iron (C4) Recent Iron Reduction in Tilled Soils (C6) Thin Muck Surface (C7) Other (Explain in Remarks) Is This Sample Area Within a Wetland? YES icators (minimum of two Sparsely Vegetated Concave Surface (B8) Drainage Patterns (B10) Moss Trim Lines (B16) Dry-Season Water Table (Q) Crayfish Burrows (C8) Saturation Visible on Aerial Imagery (C9) Stunted or Stressed Plants (D1) X Geomorphic Position (D2) Microtopographic Relief (D4) X FAC-NeutralTest(DS) Surface Water Present? yE$ Depth (inches): 3 Water Table Present? YES Depth (inches): surface Wetland Hydrology Present? Saturation Present? YES Depth (inches): surfate Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: NA one primary indicator or two 501 L present; parameter is met. YES Profile Description: Describe to the depth needed to document the indicator or confirm the absence of indicators. Depth Matrix Redox Features (in) Color (moist) % Color (moist) % Typel LocZ Texture Remarks 0-5 10YR 4 1 95 10YR 5 8 5 C M silt loam - �� �� �—IV� si ty c ay oam 'Type: C=Concentration, D=Depletion, RM=Reduced Matrix, MS=Masked Sand Grains. �Location: PL=Pore Lining, M=Matrix. Hydric Soil Indicators: Indicators for Problematic Hydric Soils3: Histosol (Al) Dark Surface (S7) 2 cm Muck (A10) Histic Epipedon (A2) Polyvalue Below Surface (58) CoaSt Prairie Redox (A16) Black Histic (A3) Thin Dark Surface (59) Piedmont Floodplain Soils (F19) Hydrogen Sulfide (A4) Loamy Gleyed Matrix (F2) Very Shallow Dark Surface (TF12) Stratified Layers (AS) X Depleted Matrix (F3) Other (Explain in Remarks) 2cm Muck (A10) Redox Dark Surface (F6) Depleted Below Dark Surface (A11) Depleted Dark Surface (F7) Thick Dark Surface (Al2) Redox Depressions (FS) 3lndicators of hydrophytic vegetation and Sandy Mucky Minerel (51) Iron-Manganese Masses (F12) wetland hydrology must be present, unless Sandy Gleyed Matrix (S4) Umbric Surface (F13) disturbed or problematic. Sandy Redox (55) Piedmont Floodplain Soils (F19) Stripped Matrix (S6) Red Parent Material (F21) Restrictive Layer (if observed): Type: ryq Hydric Soil Present? YES Depth (inches): Remarks: Indicator F3 (Depleted Matrix) present and soil meets NTCHS definition of hydric soil; parameter is met. Eastern Mountains and Piedmont Region - Version 2.0 (Adapted By: DouglasA. DeBerry, PhD, PWS, PWD) VEGETATION - Use scientific names of plants. Tree Stratum (Plot size: 30' radius ) 1. Acer rubrum 2. Liquidambar styraciflua 3. Fraxinus pennsylvanica 4. Carpinus caroliniana 5. 6. 7. Sapling Stratum (Plot size: 30' radius ) 1. 2. 3. 4. 5. 6. 7. Shrub Stratum (Plot size: 15' radius ) 1. Acer rubrum 2. Carpinus caroliniana 3. 4. 5. 6. 7. Herb Stratum (Plot size: 10' radius ) 1. Dulichium arundinaceum 2. Saururus cernuus 3. 4. S. 6. 7. 8. 9. 10. 11. 12. Woody Vines (Plot size: 30' radius ) 1. Smilax rotundifolia 2. 3. 4. 5. �� Sampling Point: DP-WD-1 %Cover Sp? Status DominanceTestWorksheet: 63 X FAC # Dominants OBL, FACW, FAC: 38 X FAC 15 FACW # Dominants across all strata: 15 FAC % Dominants OBL, FACW, FAC: Prevalencelndex Worksheet: 5 (A) 5 (B) 100% (A/B) 131 = Total Cover Total � Cover of: Multiply By: OBL 18 x 1= 18 FACW 15 x 2= 30 FAC 149 x 3= 447 FACU x 4 = UPL x5= Sum: 182 (A) 495 (B) 15 3 18 15 3 18 15 = TotalCover X FAC FAC = TotalCover X OBL OBL = TotalCover X FAC Prevalence Index = B/A = 2.72 Hydrophytic Vegetation Indicators: X Dominance Test is > 50% X Prevalence Index is <= 3.0 Problematic Hydrophytic Vegetationl �e,Pia��� Rapid Test for Hydrophytic Vegetation Morphological Adaptations 'Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Definitions of Vegetation Strata: Tf2e - Woody plants, excluding woody vines, approximately 20ft (6m) or more in height and 3in (7.6cm) or larger in diameter at breast height (DBH). $BP�IIIg - Woody plants, excluding woody vines, approximately 20ft (6m) or more in height and less than 3in (7.6cm) DBH. $hfUb - Woody plants, excluding woody vines, approximately 3 to 20ft (1 to 6m) in height. H21'b - All herbaceous (non-woody) plants, including herbaceous vines, regardless of size. Includes woody plants, except woody vines, less than approximately 3ft (lm) in height. WOOdy VIf12 - All woody vines, regardless of height. Hydrophytic Vegetation 15 = TotalCover Present? YES Remarks: (If observed, list morphological adaptations below). Indicator 2(Dominance Test) present with >50� of dominant species across all vegetation strata FAC or wetter. Eastern Mountains and Piedmont Region - Version 2.0 (Adapted By: DouglasA. DeBerry, PhD, PWS, PWD) �h� WETLAND DETERMINATION DATA FORM - Eastern Mountains and Piedmont Region DP-WD-2 Project Site: Old Carriage Road and Eastern Avenue City/County: Rocky Mount Samp. Date: 1/30/2018 Applicant/Owner: NCDOT State: NC Sampling Point: DP-WD-2 Investigator(s): 1. Thompson Section, Township, Range: Landfofm(hillslope,terrace,etc.): HIIISIOp2 Localrelief(concave,convex,none): COIlV2X Slope(%): Ot02 Subregion (LRR or MLRA): LRR P MLRA 133A Lat: 35.989749 Long: -7737314 Datum: WG584 Soil Map Unit: Meggett loam, 0-2%slopes NWI Classif.: None Are climatic/hydrologic conditions on the site typical for this time of year? Yes (If no, explain in Remarks.) Are Vegetation, Soil, or Hydrology significantly disturbed? No Normal Circumstances? Yes Are Vegetation, Soil, or Hydrology naturally problematic? No (If needed, explain any answers in Remarks.) SUMMARY OF FINDINGS - Attach site nt locations, transects, important features, etc. Hydrophytic Vegetation Present? YES Hydric Soil Present? NO Is This Sample Area Within a Wetland? NO Wetland Hydrology Present? NO Remarks: One or more parameters lacking. Area is not a wetland. Data point located up slope from DP-WD-1, about 80 ft east and slightly north. HYDROLOGY Primary Indicators (minimum of one is required; check all that a Surface Water (A1) High Water Table (A2) Saturetion (A3) Water Marks (Bl) Sediment Deposits (82) Drift Deposits (83) Algal Mat or Crust (B4) Iron Deposits (BS) Inundation Visible on Aerial (87) Water-Stained Leaves (89) Aquatic Fauna (813) True Aquatic Plants (614) Hydrogen Sulfide Odor (C1) Oxidized Rhizospheres on Living Roots (C3) Presence of Reduced Iron (C4) Recent Iron Reduction in Tilled Soils (C6) Thin Muck Surface (C7) Other (Explain in Remarks) icators (minimum of two Sparsely Vegetated Concave Surface (B8) Drainage Patterns (B10) Moss Trim Lines (B16) Dry-Season Water Table (Q) Creyfish Burrows (C8) Saturation Visible on Aerial Imagery (C9) Stunted or Stressed Plants (D1) Geomorphic Position (D2) Microtopographic Relief (D4) FAC-NeutralTest(DS) Surface Water Present? Np Depth (inches): N A Water Table Present? NO Depth (inches): >18 Wetland Hydrology Present? Saturation Present? ryp Depth (inches): �18 Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: NA ry or 501 L present; parameter is not met. NO Profile Description: Describe to the depth needed to document the indicator or confirm the absence of indicators. Depth Matrix Redox Features (in) Color (moist) % Color (moist) % Typel LocZ Texture Remarks 0-18 SYR 4 6 300 sandy clay loam 'Type: C=Concentration, D=Depletion, RM=Reduced Matrix, MS=Masked Sand Grains. �Location: PL=Pore Lining, M=Matrix. Hydric Soil Indicators: Indicators for Problematic Hydric Soils3: Histosol (Al) Dark Surface (S7) 2 cm Muck (A10) Histic Epipedon (A2) Polyvalue Below Surface (58) CoaSt Prairie Redox (A16) Black Histic (A3) Thin Dark Surface (59) Piedmont Floodplain Soils (F19) Hydrogen Sulfide (A4) Loamy Gleyed Matrix (F2) Very Shallow Dark Surface (TF12) Stratified Layers (AS) Depleted Matrix (F3) Other (Explain in Remarks) 2cm Muck (A10) Redox Dark Surface (F6) Depleted Below Dark Surface (A11) Depleted Dark Surface (F7) Thick Dark Surface (Al2) Redox Depressions (FS) 3lndicators of hydrophytic vegetation and Sandy Mucky Minerel (51) Iron-Manganese Masses (F12) wetland hydrology must be present, unless Sandy Gleyed Matrix (S4) Umbric Surface (F13) disturbed or problematic. Sandy Redox (55) Piedmont Floodplain Soils (F19) Stripped Matrix (S6) Red Parent Material (F21) Restrictive Layer (if observed): Type: ryq Hydric Soil Present? NO Depth (inches): Remarks: No hydric soil indicators present and soil does not meet NTCHS definition of hydric soil; parameter is not met. Eastern Mountains and Piedmont Region - Version 2.0 (Adapted By: DouglasA. DeBerry, PhD, PWS, PWD) VEGETATION - Use scientific names of plants. Tree Stratum (Plot size: 30' radius ) 1. Liriodendron tulipifera 2. Quercus alba 3. Acer rubrum 4. Carya tomentosa 5. 6. 7. Sapling Stratum (Plot size: 1. 2. 3. 4. 5. 6. 7. Shrub Stratum (Plot size: 1. Carpinus caroliniana 2. Fagus grandifolia 3. 4. 5. 6. 7. Herb Stratum (Plot size: 1. Carex glaucodea 2. 3. 4. S. 6. 7. 8. 9. 10. 11. 12. Woody Vines (Plot size: 1. Smilax rotundifolia 2. Smilax smallii 3. 4. 5. �� Sampling Point: DP-WD-2 %Cover Sp? Status DominanceTestWorksheet: 63 X FACU # Dominants OBL, FACW, FAC: 63 X FACU 38 X FAC # Dominants across all strata: 15 UPL % Dominants OBL, FACW, FAC: Prevalencelndex Worksheet: 4 (A) 7 (B) 57� (A/B) 179 = Total Cover Total � Cover of: Multiply By: 30' radius ) OBL x 1= FACW x 2 = FAC 106 x 3= 318 FACU 144 x 4= 576 UPL 15 x 5= 75 Sum: 265 (A) 969 (B) 15' radius ) 10' radius ) 30' radius ) 38 15 53 15 15 15 3 18 = TotalCover X FAC X FACU = TotalCover X FAC Prevalence Index = B/A = 3.66 Hydrophytic Vegetation Indicators: X Dominance Test is > 50% Prevalence Index is <= 3.0 Problematic Hydrophytic Vegetationl �e,Pia��� Rapid Test for Hydrophytic Vegetation Morphological Adaptations 'Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Definitions of Vegetation Strata: Tf2e - Woody plants, excluding woody vines, approximately 20ft (6m) or more in height and 3in (7.6cm) or larger in diameter at breast height (DBH). $BP�IIIg - Woody plants, excluding woody vines, approximately 20ft (6m) or more in height and less than 3in (7.6cm) DBH. $hfUb - Woody plants, excluding woody vines, approximately 3 to 20ft (1 to 6m) in height. H21'b - All herbaceous (non-woody) plants, including herbaceous vines, regardless of size. Includes woody plants, except woody vines, less than approximately 3ft (lm) in height. = TotalCover X FAC FACU WOOCJy VIf12 - All woody vines, regardless of height. Hydrophytic Vegetation = TotalCover Present? YES Remarks: (If observed, list morphological adaptations below). Indicator 2(Dominance Test) present with >50� of dominant species across all vegetation strata FAC or wetter. Eastern Mountains and Piedmont Region - Version 2.0 (Adapted By: DouglasA. DeBerry, PhD, PWS, PWD) `�h� WETLAND DETERMINATION DATA FORM - Eastern Mountains and Piedmont Region DP-WE-1 Project Site: Old Carriage Road and Eastern Avenue City/County: Rocky Mount Samp. Date: 1/30/2018 Applicant/Owner: NCDOT State: NC Sampling Point: DP-WE-1 Investigator(s): 1. Thompson Section, Township, Range: Landform (n�nSioPe, cerra�e, ec�.): Bottomland Swamp Local relief (concave, convex, none): �oncave Slope (%): O to 2 Subregion (LRR or MLRA): LRR P MLRA 133A Lat: 35.989613 Long: -7737314 Datum: WG584 Soil Map Unit: Meggett loam, 0-2%slopes NWI Classif.: PF01C Are climatic/hydrologic conditions on the site typical for this time of year? Yes (If no, explain in Remarks.) Are Vegetation, Soil, or Hydrology significantly disturbed? No Normal Circumstances? Yes Are Vegetation, Soil, or Hydrology naturally problematic? No (If needed, explain any answers in Remarks.) SUMMARY OF FINDINGS - Attach site ma nt locations, transects, important features, etc. Hydrophytic Vegetation Present? YES Hydric Soil Present? YES Is This Sample Area Within a Wetland? YES Wetland Hydrology Present? YES Remarks: All parameters are met. Area is classified as a palustrine forested (PFO) wetland. Data point located on west side of driveway, directly south of wetland flag WE3. HYDROLOGY Primary Indicators (minimum of one is required; check all that a Surface Water (A1) High Water Table (A2) Saturation (A3) Water Marks (Bl) Sediment Deposits (82) Drift Deposits (83) Algal Mat or Crust (64) Iron Deposits (BS) Inundation Visible on Aerial (B7) Water-Stained Leaves (69) Aquatic Fauna (813) True Aquatic Plants (614) Hydrogen Sulfide Odor (C1) Oxidized Rhizospheres on Living Roots (C3) Presence of Reduced Iron (C4) Recent Iron Reduction in Tilled Soils (C6) Thin Muck Surface (C7) Other (Explain in Remarks) icators (minimum of two Sparsely Vegetated Concave Surface (B8) Drainage Patterns (B10) Moss Trim Lines (616) Dry-Season Water Table (Q) Crayfish Burrows (C8) Saturation Visible on Aerial Imagery (C9) Stunted or Stressed Plants (D1) X Geomorphic Position (D2) Microtopogrephic Relief (D4) X FAC-Neutral Test (DS) Surface Water Present? YES Depth (inches): ( Water Table Present? YES Depth (inches): surface Wetland Hydrology Present? Saturation Present? YES Depth (inches): surfate Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: NA At least one primary indicator or two secorn Unidentified fish observed in surface water. 501 L present; parameter is met. YES Profile Description: Describe to the depth needed to document the indicator or confirm the absence of indicators. Depth Matrix Redox Features (in) Color (moist) % Color (moist) % Typel LocZ Texture Remarks 0-6 10YR 5 2 300 silty clay - �� —� �—IV� si ty c ay oam 'Type: C=Concentration, D=Depletion, RM=Reduced Matrix, MS=Masked Sand Grains. �Location: PL=Pore Lining, M=Matrix. Hydric Soil Indicators: Indicators for Problematic Hydric Soils3: Histosol (Al) Dark Surface (S7) 2 cm Muck (A10) Histic Epipedon (A2) Polyvalue Below Surface (SS) CoaSt PI'ail'ie Redox (A16) Black Histic (A3) Thin Dark Surface (59) Piedmont Floodplain Soils (F19) Hydrogen Sulfide (A4) Loamy Gleyed Matrix (F2) Very Shallow Dark Surface (TF12) Stratified Layers (AS) X Depleted Matrix (F3) Other (Explain in Remarks) 2cm Muck (A10) Redox Dark Surface (F6) Depleted Below Dark Surface (A11) Depleted Dark Surface (F7) Thick Dark Surface (Al2) Redox Depressions (F8) 3lndicators of hydrophytic vegetation and Sandy Mucky Minerel (51) Iron-Manganese Masses (F12) wetland hydrology must be present, unless Sandy Gleyed Matrix (54) Umbric Surface (F13) disturbed or problematic. Sandy Redox (SS) Piedmont Floodplain Soils (F19) Stripped Matrix (56) Red Parent Material (F21) Restrictive Layer (if observed): Type: ryq Hydric Soil Present? YES Depth (inches): Remarks: Indicator F3 (Depleted Matrix) present and soil meets NTCHS definition of hydric soil; parameter is met. Soil unconsolidated beneath 12 inches. Irretrievable with soil auger. Also appeared to be silty clay loam. Eastern Mountains and Piedmont Region - Version 2.0 (Adapted By: Douglas A. DeBerry, PhD, PWS, PWD) VEGETATION - Use scientific names of plants. Tree Stratum (Plot size: 30' radius ) 1. Acer rubrum 2. Salix nigra 3. Fraxinus pennsylvanica 4. Carpinus caroliniana 5. Diospyros virginiana 6. Betula nigra 7. Sapling Stratum (Plot size: 30' radius ) 1. 2. 3. 4. 5. 6. 7. Shrub Stratum (Plot size: 15' radius ) 1. Acer rubrum 2. 3. 4. 5. 6. 7. Herb Stratum (Plot size: 10' radius ) 1. Stellaria media 2. Symphyotrichum lateriflorum 3. 4. S. 6. 7. 8. 9. 10. 11. 12. Woody Vines (Plot size: 30' radius ) 1. 2. 3. 4. 5. �� Sampling Point: DP-WE-1 %Cover Sp? Status DominanceTestWorksheet: 63 X FAC # Dominants OBL, FACW, FAC: 4 (A) 63 X OBL 38 FACW # Dominants across all strata: 5 (B) 15 FAC 15 FAC % Dominants OBL, FACW, FAC: 80% (A/B) 3 FACW Prevalencelndex Worksheet: 197 = Total Cover Total % Cover of: Multiply By: OBL 63 x 1= 63 FACW 44 x 2= 88 FAC 108 x 3= 324 FACU x 4 = UPL 3 x5= 15 Sum: 218 (A) 490 (B) Prevalence Index = B/A = 2.25 = Total Cover Hydrophytic Vegetation Indicators: X Dominance Test is > 50% 15 X FAC X Prevalence Index is <= 3.0 Problematic Hydrophytic Vegetationl �e,Pia��� Rapid Test for Hydrophytic Vegetation Morphological Adaptations 'Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Definitions of Vegetation Strata: 15 = Total Cover Tf2e - Woody plants, excluding woody vines, approximately 20k (6m) or 3 X UPL more in height and 3in (7.6cm) or larger in diameter at breast height (DBH). 3 X FACW $BP�IfIg - Woody plants, excluding woody vines, approximately 20ft (6m) or more in height and less than 3in (7.6cm) DBH. $hfUb - Woody plants, excluding woody vines, approximately 3 to 20k (1 to 6m) in height. H21'b - All herbaceous (non-woody) plants, including herbaceous vines, regardless of size. Includes woody plants, except woody vines, less than approximately 3ft (1m) in height. 6 = Total Cover WOOdy VIf12 - All woody vines, regardless of height. Hydrophytic Vegetation = TotalCover Present? YES Remarks: (If observed, list morphological adaptations below). Indicator 2(Dominance Test) present with >50� of dominant species across all vegetation strata FAC or wetter. Eastern Mountains and Piedmont Region - Version 2.0 (Adapted By: Douglas A. DeBerry, PhD, PWS, PWD) �h� WETLAND DETERMINATION DATA FORM - Eastern Mountains and Piedmont Region DP-WE-2 Project Site: Old Carriage Road and Eastern Avenue City/County: Rocky Mount Samp. Date: 1/30/2018 Applicant/Owner: NCDOT State: NC Sampling Point: DP-WE-2 Investigator(s): 1. Thompson Section, Township, Range: Landform (n�nSioPe, cerra�e, ec�.): Terrace Local relief (concave, convex, none): �onvex Slope (%): 2 to 5 Subregion (LRR or MLRA): LRR P MLRA 133A Lat: 35.989523 Long: -7737314 Datum: WG584 Soil Map Unit: Meggett loam, 0-2%slopes NWI Classif.: PF01C Are climatic/hydrologic conditions on the site typical for this time of year? Yes (If no, explain in Remarks.) Are Vegetation, Soil, or Hydrology significantly disturbed? No Normal Circumstances? Yes Are Vegetation, Soil, or Hydrology naturally problematic? No (If needed, explain any answers in Remarks.) SUMMARY OF FINDINGS - Attach site nt locations, transects, important features, etc. Hydrophytic Vegetation Present? NO Hydric Soil Present? NO Is This Sample Area Within a Wetland? NO Wetland Hydrology Present? NO Remarks: One or more parameters lacking. Area is not a wetland. Data point located west of driveway and north of road, directly south of wetland flag WE-4. HYDROLOGY Primary Indicators (minimum of one is required; check all that a Surface Water (A1) High Water Table (A2) Saturetion (A3) Water Marks (Bl) Sediment Deposits (82) Drift Deposits (83) Algal Mat or Crust (B4) Iron Deposits (BS) Inundation Visible on Aerial (87) Water-Stained Leaves (89) Aquatic Fauna (813) True Aquatic Plants (614) Hydrogen Sulfide Odor (C1) Oxidized Rhizospheres on Living Roots (C3) Presence of Reduced Iron (C4) Recent Iron Reduction in Tilled Soils (C6) Thin Muck Surface (C7) Other (Explain in Remarks) icators (minimum of two Sparsely Vegetated Concave Surface (B8) Drainage Patterns (B10) Moss Trim Lines (B16) Dry-Season Water Table (Q) Creyfish Burrows (C8) Saturation Visible on Aerial Imagery (C9) Stunted or Stressed Plants (D1) Geomorphic Position (D2) Microtopographic Relief (D4) FAC-NeutralTest(DS) Surface Water Present? Np Depth (inches): NA Water Table Present? NO Depth (inches): >18 Wetland Hydrology Present? Saturation Present? ryp Depth (inches): �18 Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: NA ry or 501 L present; parameter is not met. NO Profile Description: Describe to the depth needed to document the indicator or confirm the absence of indicators. Depth Matrix Redox Features (in) Color (moist) % Color (moist) % Typel LocZ Texture Remarks 0-6 7.SYR 4 3 300 clay loam - �� 'Type: C=Concentration, D=Depletion, RM=Reduced Matrix, MS=Masked Sand Grains. �Location: PL=Pore Lining, M=Matrix. Hydric Soil Indicators: Indicators for Problematic Hydric Soils3: Histosol (Al) Dark Surface (S7) 2 cm Muck (A10) Histic Epipedon (A2) Polyvalue Below Surface (58) CoaSt Prairie Redox (A16) Black Histic (A3) Thin Dark Surface (59) Piedmont Floodplain Soils (F19) Hydrogen Sulfide (A4) Loamy Gleyed Matrix (F2) Very Shallow Dark Surface (TF12) Stratified Layers (AS) Depleted Matrix (F3) Other (Explain in Remarks) 2cm Muck (A10) Redox Dark Surface (F6) Depleted Below Dark Surface (A11) Depleted Dark Surface (F7) Thick Dark Surface (Al2) Redox Depressions (FS) 3lndicators of hydrophytic vegetation and Sandy Mucky Minerel (51) Iron-Manganese Masses (F12) wetland hydrology must be present, unless Sandy Gleyed Matrix (S4) Umbric Surface (F13) disturbed or problematic. Sandy Redox (55) Piedmont Floodplain Soils (F19) Stripped Matrix (S6) Red Parent Material (F21) Restrictive Layer (if observed): Type: ryq Hydric Soil Present? NO Depth (inches): Remarks: No hydric soil indicators present and soil does not meet NTCHS definition of hydric soil; parameter is not met. Eastern Mountains and Piedmont Region - Version 2.0 (Adapted By: DouglasA. DeBerry, PhD, PWS, PWD) VEGETATION - Use scientific names of plants. �� Sampling Point: DP-WE-2 Tree Stratum (Plot size: 30' radius ) 1. Acer rubrum 2. Fraxinus pennsylvanica 3. 4. 5. 6. 7. Sapling Stratum (Plot size: 30' radius ) 1. 2. 3. 4. 5. 6. 7. Shrub Stratum (Plot size: 15' radius ) 1. Quercus velutina 2. 3. 4. 5. 6. 7. Herb Stratum (Plot size: 10' radius ) 1. Stellaria media 2. Allium vineale 3. Ilex opaca 4. S. 6. 7. 8. 9. 10. 11. 12. Woody Vines (Plot size: 30' radius ) 1. 2. 3. 4. 5. %Cover Sp? Status DominanceTestWorksheet: 38 X FAC # Dominants OBL, FACW, FAC: 2 (A) 38 X FACW # Dominants across all strata: 4 (B) % Dominants OBL, FACW, FAC: 50% (A/B) Prevalencelndex Worksheet: 76 = Total Cover Total % Cover of: Multiply By: OBL x 1 = FACW 38 x 2= 76 FAC 38 x 3= 114 FACU 18 x 4= 72 UPL 78 x 5= 390 Su m: 172 (A) 652 (B) Prevalence Index = B/A = 3.79 = Total Cover Hydrophytic Vegetation Indicators: Dominance Test is > 50% 15 X UPL Prevalence Index is <= 3.0 Problematic Hydrophytic Vegetationl �e,Pia��� Rapid Test for Hydrophytic Vegetation Morphological Adaptations 'Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Definitions of Vegetation Strata: 15 = TotalCover Tf2e - Woody plants, excluding woody vines, approximately 20ft (6m) or 63 X �JP� more in height and 3in (7.6cm) or larger in diameter at breast height (DBH). 15 FACU 3 FACU $BP�IIIg - Woody plants, excluding woody vines, approximately 20ft (6m) or more in height and less than 3in (7.6cm) DBH. $hfUb - Woody plants, excluding woody vines, approximately 3 to 20ft (1 to 6m) in height. H21'b - All herbaceous (non-woody) plants, including herbaceous vines, regardless of size. Includes woody plants, except woody vines, less than approximately 3ft (lm) in height. 81 = TotalCover Remarks: (If observed, list morphological adaptations below). No hydrophytic vegetation indicators present; parameter is not met. WOOdy VIf12 - All woody vines, regardless of height. Hydrophytic Vegetation = Total Cover Present? NO Eastern Mountains and Piedmont Region - Version 2.0 (Adapted By: DouglasA. DeBerry, PhD, PWS, PWD) USACE AID # Project Name ApplicanUOwner Name Wetland Type Level III Ecoregion River Basin County � Yes ❑ No NC WAM FIELD ASSESSMENT FORM Accompanies User Manual Version 5.0 NCDWR# U-5996 Eastern Ave. and Old Date of Evaluation 4/19/2018 Carriage Road NCDOT Wetland Site Name WA Headwater Forest Assessor Name/Organization Sean Murray, VHB Piedmont Nearest Named Water Body Stony Creek Tar-Pamlico USGS 8-Digit Catalogue Unit 03020101 Nash NCDWR Region Raleigh Precipitation within 48 hrs? Latitude/Lonqitude (deci-deqrees) 35.971106/-77.931769 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.) • HabitaUplant 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 floodinq durinq 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 z 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. �<_ 15-feet wide ❑> 15-feet wide ❑ Other open water (no tributary present) 7d. Do roots of assessment area vegetation extend into the bank of the tributary/open water? �Yes ❑No 7e. Is stream or other open water sheltered or exposed? �Sheltered — adjacent open water with width < 2500 feet and no regular boat traffic. ❑Exposed — adjacent open water with width >_ 2500 feet or regular boat traffic. 8. Wetland Width at the Assessment Area — wetland type/wetland complex condition metric (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 ❑I ❑I ❑I From 0.1 to < 0.5 acre ❑J ❑J ❑J From 0.01 to < 0.1 acre ❑K ❑K ❑K < 0.01 acre or assessment area is clear-cut 12. Wetland Intactness — wetland type condition metric (evaluate for Pocosins only) ❑A Pocosin is the full extent (>_ 90%) of its natural landscape size. ❑B Pocosin type is < 90% of the full extent of its natural landscape size. 13. Connectivity to Other Natural Areas — landscape condition metric 13a. Check appropriate box(es) (a box may be checked in each column). Involves a GIS effort with field adjustment. This metric evaluates whether the wetland is well connected (Well) and/or loosely connected (Loosely) to the landscape patch, the contiguous naturally vegetated area and open water (if appropriate). Boundaries are formed by four-lane roads, 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. a AA VVl' 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 � ❑B ❑B Moderate density mid-story/sapling layer ��C �C Mid-story/sapling layer sparse or absent � ❑A ❑A Dense shrub layer � �B �B Moderate density shrub layer �❑C ❑C Shrub layer sparse or absent � ❑A ❑A Dense herb layer _ ❑B ❑B Moderate density herb layer �C �C Herb layer sparse or absent 18. Snags — wetland type condition metric (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 DBN. ❑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 NotA 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 � � � �''l, � �'`'� t 1 }��a.J���` ' . - Pr �' �,.J T �f 'l� y"� �'' ��� a E. 1� i'�� � ���}yw °+��. l��' s t� p y I '��� `j�� � "�i�l ! �" '�'� ��°ly �y`� '�.��� ;Mq��, �� � V k P v� , � �I �'� , 1� ��,'" � �� `i i i�t � �� �[• �.,�'J � � � � � `,c r� �t °� ,i �y� °.� �r, �`! \ �'' " � � � ,'fH •�,,.c.�- �� ��_ � #, ` .,�rr �_ r �:�.� �"�'�z'r `'�..,..% ``-�. N ��..�' �.�, / 22. Hydrologic Connectivity — assessment area condition metric (evaluate for riparian wetlands and SaltlBrackish 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 Assessment Area WA consists of bottomland hardwood forest bordered on the north by forested wetland and on the south, east, and west by residential and commercial development and roads. The west side is bounded by a stream. The wetland appears generally undisturbed with a small amount of exotic species recruitment. See photographs in Attachment A. NC WAM Wetland Rating Sheet Accompanies User Manual Version 5.0 Wetland Site Name WA Wetland Type Headwater Forest Date of Assessment 4/19/2018 Assessor Name/Organization Sean Murray, VHB Notes on Field Assessment Form (Y/N) Presence of regulatory considerations (Y/N) 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) Assessment area experiences overbank flooding during normal rainfall conditions (Y/N) Assessment area is on a coastal island (Y/N) YES YES YES NO NO NO Sub-function Rating Summary 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 HIGH Condition/Opportunity HIGH Opportunity Presence (Y/N) YES Pollution Change Condition NA Condition/Opportunity NA Opportunity Presence (Y/N) NA Habitat Physical Structure Condition MEDIUM Landscape Patch Structure Condition HIGH Vegetation Composition Condition MEDIUM Function Rating Summary Function Metrics Rating Hydrology Condition HIGH Water Quality Condition HIGH Condition/Opportunity HIGH Opportunity Presence (Y/N) YES Habitat Condition HIGH Overall Wetland Rating HIGH USACE AID # Project Name ApplicanUOwner Name Wetland Type Level III Ecoregion River Basin County � Yes ❑ No NC WAM FIELD ASSESSMENT FORM Accompanies User Manual Version 5.0 NCDWR# U-5996 Eastern Ave. and Old Date of Evaluation 4/19/2018 Carriage Road NCDOT Wetland Site Name WB Riverine Swamp Forest Assessor Name/Organization Sean Murray, VHB Piedmont Nearest Named Water Body Stony Creek Tar-Pamlico USGS 8-Digit Catalogue Unit 03020101 Nash NCDWR Region Raleigh Precipitation within 48 hrs? Latitude/Lonqitude (deci-deqrees) 35.988690/-77.901478 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.) • HabitaUplant 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 floodinq durinq 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 z 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. ❑<_ 15-feet wide �> 15-feet wide ❑ Other open water (no tributary present) 7d. Do roots of assessment area vegetation extend into the bank of the tributary/open water? �Yes ❑No 7e. Is stream or other open water sheltered or exposed? �Sheltered — adjacent open water with width < 2500 feet and no regular boat traffic. ❑Exposed — adjacent open water with width >_ 2500 feet or regular boat traffic. 8. Wetland Width at the Assessment Area — wetland type/wetland complex condition metric (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 ❑I ❑I ❑I From 0.1 to < 0.5 acre ❑J ❑J ❑J From 0.01 to < 0.1 acre ❑K ❑K ❑K < 0.01 acre or assessment area is clear-cut 12. Wetland Intactness — wetland type condition metric (evaluate for Pocosins only) ❑A Pocosin is the full extent (>_ 90%) of its natural landscape size. ❑B Pocosin type is < 90% of the full extent of its natural landscape size. 13. Connectivity to Other Natural Areas — landscape condition metric 13a. Check appropriate box(es) (a box may be checked in each column). Involves a GIS effort with field adjustment. This metric evaluates whether the wetland is well connected (Well) and/or loosely connected (Loosely) to the landscape patch, the contiguous naturally vegetated area and open water (if appropriate). Boundaries are formed by four-lane roads, 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. a 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 � ❑B ❑B Moderate density mid-story/sapling layer ��C �C Mid-story/sapling layer sparse or absent -� ❑A ❑A Dense shrub layer � ❑B ❑B Moderate density shrub layer ��C �C Shrub layer sparse or absent � ❑A ❑A Dense herb layer _ �B �B Moderate density herb layer ❑C ❑C Herb layer sparse or absent 18. Snags — wetland type condition metric (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 alt 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 NotA 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 � � � �,,,, f = ,-� r" �.�—... T -�. ,'� �.-.� , =�;� ;�� �v /'�',�'•�n.y�-�-.�;y,. . P", '�'',� z s � ., �j, ; • "� �i ,i a V � � �- � � � ,� , i '� r 4 c� ,�ry, r t�. � �,"� � l� _ ��;�� � �,��'+,� �, '� �.., � ,� i� 4'� ��- `_'� �\1:1''I J ° '� �r�', � .,.�f�"'S'� ` '�� �) � , � r(Ci •�.,.��: / y f: `•`..�_..`'"'�..'�� ����; •ti'_..� ��'!� 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 Assessment Area WB consists of riverine swamp forest bordered on the north by residential and road development and on the south by agriculture and upland forest. Stony Creek flows, from west to east, through the center. A portion of the wetland has been filled for a road/bridge. Large amounts of sediment had been deposited on the stream banks in the past. This sediment is now covered with mostly upland vegetation including trees 15 to 20 years old. Also a powerline easement has been cleared through the wetland, and a vehicle trail is located within the easement. See photographs in Attachment A. NC WAM Wetland Rating Sheet Accompanies User Manual Version 5.0 Wetland Site Name WB Date of Assessment 4/19/2018 Wetland Type Riverine Swamp Forest Assessor Name/Organization Sean Murray, VHB Notes on Field Assessment Form (Y/N) Presence of regulatory considerations (Y/N) 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) Assessment area experiences overbank flooding during normal rainfall conditions (Y/N) Assessment area is on a coastal island (Y/N) YES YES YES NO NO NO Sub-function Rating Summary Function Sub-function Metrics Rating Hydrology Surface Storage and Retention Condition LOW Sub-surface Storage and Retention Condition MEDIUM Water Quality Pathogen Change Condition LOW Condition/Opportunity LOW Opportunity Presence (Y/N) NO Particulate Change Condition LOW Condition/Opportunity LOW Opportunity Presence (Y/N) YES Soluble Change Condition MEDIUM Condition/Opportunity HIGH Opportunity Presence (Y/N) YES Physical Change Condition HIGH Condition/Opportunity HIGH Opportunity Presence (Y/N) YES Pollution Change Condition NA Condition/Opportunity NA Opportunity Presence (Y/N) NA Habitat Physical Structure Condition MEDIUM Landscape Patch Structure Condition HIGH Vegetation Composition Condition MEDIUM Function Rating Summary Function Metrics Rating Hydrology Condition LOW Water Quality Condition MEDIUM Condition/Opportunity HIGH Opportunity Presence (Y/N) YES Habitat Condition HIGH Overall Wetland Rating MEDIUM USACE AID # Project Name ApplicanUOwner Name Wetland Type Level III Ecoregion River Basin County � Yes ❑ No NC WAM FIELD ASSESSMENT FORM Accompanies User Manual Version 5.0 NCDWR# U-5996 Eastern Ave. and Old Date of Evaluation 4/19/2018 Carriage Road NCDOT Wetland Site Name WC Riverine Swamp Forest Assessor Name/Organization Sean Murray, VHB Piedmont Nearest Named Water Body Stony Creek Tar-Pamlico USGS 8-Digit Catalogue Unit 03020101 Nash NCDWR Region Raleigh Precipitation within 48 hrs? Latitude/Lonqitude (deci-deqrees) 35.989094/-77.902826 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.) • HabitaUplant 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 floodinq durinq 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 z 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. ❑<_ 15-feet wide �> 15-feet wide ❑ Other open water (no tributary present) 7d. Do roots of assessment area vegetation extend into the bank of the tributary/open water? �Yes ❑No 7e. Is stream or other open water sheltered or exposed? �Sheltered — adjacent open water with width < 2500 feet and no regular boat traffic. ❑Exposed — adjacent open water with width >_ 2500 feet or regular boat traffic. 8. Wetland Width at the Assessment Area — wetland type/wetland complex condition metric (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 ❑I ❑I ❑I From 0.1 to < 0.5 acre ❑J ❑J ❑J From 0.01 to < 0.1 acre ❑K ❑K ❑K < 0.01 acre or assessment area is clear-cut 12. Wetland Intactness — wetland type condition metric (evaluate for Pocosins only) ❑A Pocosin is the full extent (>_ 90%) of its natural landscape size. ❑B Pocosin type is < 90% of the full extent of its natural landscape size. 13. Connectivity to Other Natural Areas — landscape condition metric 13a. Check appropriate box(es) (a box may be checked in each column). Involves a GIS effort with field adjustment. This metric evaluates whether the wetland is well connected (Well) and/or loosely connected (Loosely) to the landscape patch, the contiguous naturally vegetated area and open water (if appropriate). Boundaries are formed by four-lane roads, 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. a 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 � ❑B ❑B Moderate density mid-story/sapling layer ��C �C Mid-story/sapling layer sparse or absent -� ❑A ❑A Dense shrub layer � ❑B ❑B Moderate density shrub layer ��C �C Shrub layer sparse or absent � ❑A ❑A Dense herb layer _ �B �B Moderate density herb layer ❑C ❑C Herb layer sparse or absent 18. Snags — wetland type condition metric (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 alt 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 NotA 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 � � � �,,,, f = ,-� r" �.�—... T -�. ,'� �.-.� , =�;� ;�� �v /'�',�'•�n.y�-�-.�;y,. . P", '�'',� z s � ., �j, ; • "� �i ,i a V � � �- � � � ,� , i '� r 4 c� ,�ry, r t�. � �,"� � l� _ ��;�� � �,��'+,� �, '� �.., � ,� i� 4'� ��- `_'� �\1:1''I J ° '� �r�', � .,.�f�"'S'� ` '�� �) � , � r(Ci •�.,.��: / y f: `•`..�_..`'"'�..'�� ����; •ti'_..� ��'!� 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 Assessment Area WC consists of riverine swamp forest bordered on the north by residential and road development and on the south by agriculture and upland forest. Stony Creek flows, from west to east, through the center. The wetland edge on the north side has been filled for road construction. Moderate amounts of sediment had been deposited on the stream banks within the assessment area. This sediment is now covered with vegetation including trees 15 to 20 years old. See photographs in Attachment A. NC WAM Wetland Rating Sheet Accompanies User Manual Version 5.0 Wetland Site Name WC Date of Assessment 4/19/2018 Wetland Type Riverine Swamp Forest Assessor Name/Organization Sean Murray, VHB Notes on Field Assessment Form (Y/N) Presence of regulatory considerations (Y/N) 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) Assessment area experiences overbank flooding during normal rainfall conditions (Y/N) Assessment area is on a coastal island (Y/N) YES YES NO YES NO NO NO Sub-function Rating Summary Function Sub-function Metrics Rating Hydrology Surface Storage and Retention Condition MEDIUM Sub-surface Storage and Retention Condition MEDIUM Water Quality Pathogen Change Condition MEDIUM Condition/Opportunity MEDIUM Opportunity Presence (Y/N) NO Particulate Change Condition LOW Condition/Opportunity LOW Opportunity Presence (Y/N) NO Soluble Change Condition LOW Condition/Opportunity LOW Opportunity Presence (Y/N) NO Physical Change Condition MEDIUM Condition/Opportunity MEDIUM Opportunity Presence (Y/N) NO Pollution Change Condition NA Condition/Opportunity NA Opportunity Presence (Y/N) NA Habitat Physical Structure Condition MEDIUM Landscape Patch Structure Condition HIGH Vegetation Composition Condition HIGH Function Rating Summary Function Metrics Rating Hydrology Condition MEDIUM Water Quality Condition LOW Condition/Opportunity LOW Opportunity Presence (Y/N) NO Habitat Condition HIGH Overall Wetland Rating MEDIUM USACE AID # Project Name ApplicanUOwner Name Wetland Type Level III Ecoregion River Basin County � Yes ❑ No NC WAM FIELD ASSESSMENT FORM Accompanies User Manual Version 5.0 NCDWR# U-5996 Eastern Ave. and Old Date of Evaluation 4/19/2018 Carriage Road NCDOT Wetland Site Name WD Riverine Swamp Forest Assessor Name/Organization Sean Murray, VHB Piedmont Nearest Named Water Body Stony Creek Tar-Pamlico USGS 8-Digit Catalogue Unit 03020101 Nash NCDWR Region Raleigh Precipitation within 48 hrs? Latitude/Lonqitude (deci-deqrees) 35.989692/-77.902592 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.) • HabitaUplant 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 floodinq durinq 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 z 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. ❑<_ 15-feet wide ❑> 15-feet wide ❑ Other open water (no tributary present) 7d. Do roots of assessment area vegetation extend into the bank of the tributary/open water? ❑Yes ❑No 7e. Is stream or other open water sheltered or exposed? ❑Sheltered — adjacent open water with width < 2500 feet and no regular boat traffic. ❑Exposed — adjacent open water with width >_ 2500 feet or regular boat traffic. 8. Wetland Width at the Assessment Area — wetland type/wetland complex condition metric (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 ❑I ❑I ❑I From 0.1 to < 0.5 acre ❑J ❑J ❑J From 0.01 to < 0.1 acre ❑K ❑K ❑K < 0.01 acre or assessment area is clear-cut 12. Wetland Intactness — wetland type condition metric (evaluate for Pocosins only) ❑A Pocosin is the full extent (>_ 90%) of its natural landscape size. ❑B Pocosin type is < 90% of the full extent of its natural landscape size. 13. Connectivity to Other Natural Areas — landscape condition metric 13a. Check appropriate box(es) (a box may be checked in each column). Involves a GIS effort with field adjustment. This metric evaluates whether the wetland is well connected (Well) and/or loosely connected (Loosely) to the landscape patch, the contiguous naturally vegetated area and open water (if appropriate). Boundaries are formed by four-lane roads, 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. a 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 � ❑B ❑B Moderate density mid-story/sapling layer ��C �C Mid-story/sapling layer sparse or absent -� ❑A ❑A Dense shrub layer � ❑B ❑B Moderate density shrub layer ��C �C Shrub layer sparse or absent � ❑A ❑A Dense herb layer _ �B �B Moderate density herb layer ❑C ❑C Herb layer sparse or absent 18. Snags — wetland type condition metric (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 alt 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 NotA 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 � � � �,,,, f = ,-� r" �.�—... T -�. ,'� �.-.� , =�;� ;�� �v /'�',�'•�n.y�-�-.�;y,. . P", '�'',� z s � ., �j, ; • "� �i ,i a V � � �- � � � ,� , i '� r 4 c� ,�ry, r t�. � �,"� � l� _ ��;�� � �,��'+,� �, '� �.., � ,� i� 4'� ��- `_'� �\1:1''I J ° '� �r�', � .,.�f�"'S'� ` '�� �) � , � r(Ci •�.,.��: / y f: `•`..�_..`'"'�..'�� ����; •ti'_..� ��'!� 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 Assessment Area WD consists of riverine swamp forest bordered on the north by residential development and on the east, south, and west by roads and private driveways. The driveway on the west side separates this assessment area from the Pig Basket Creek wetland system. See photographs in Attachment A. NC WAM Wetland Rating Sheet Accompanies User Manual Version 5.0 Wetland Site Name WD Date of Assessment 4/19/2018 Wetland Type Riverine Swamp Forest Assessor Name/Organization Sean Murray, VHB Notes on Field Assessment Form (Y/N) Presence of regulatory considerations (Y/N) 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) Assessment area experiences overbank flooding during normal rainfall conditions (Y/N) Assessment area is on a coastal island (Y/N) YES YES NO NO NO NO NO Sub-function Rating Summary Function Sub-function Metrics Rating Hydrology Surface Storage and Retention Condition MEDIUM Sub-surface Storage and Retention Condition MEDIUM Water Quality Pathogen Change Condition MEDIUM Condition/Opportunity MEDIUM Opportunity Presence (Y/N) NO Particulate Change Condition MEDIUM Condition/Opportunity MEDIUM Opportunity Presence (Y/N) NO Soluble Change Condition LOW Condition/Opportunity LOW Opportunity Presence (Y/N) NO Physical Change Condition LOW Condition/Opportunity LOW Opportunity Presence (Y/N) NO Pollution Change Condition NA Condition/Opportunity NA Opportunity Presence (Y/N) NA Habitat Physical Structure Condition MEDIUM Landscape Patch Structure Condition LOW Vegetation Composition Condition HIGH Function Rating Summary Function Metrics Rating Hydrology Condition MEDIUM Water Quality Condition LOW Condition/Opportunity LOW Opportunity Presence (Y/N) NO Habitat Condition MEDIUM Overall Wetland Rating MEDIUM USACE AID # Project Name ApplicanUOwner Name Wetland Type Level III Ecoregion River Basin County � Yes ❑ No NC WAM FIELD ASSESSMENT FORM Accompanies User Manual Version 5.0 NCDWR# U-5996 Eastern Ave. and Old Date of Evaluation 4/19/2018 Carriage Road NCDOT Wetland Site Name WE Riverine Swamp Forest Assessor Name/Organization Sean Murray, VHB Piedmont Nearest Named Water Body Stony Creek Tar-Pamlico USGS 8-Digit Catalogue Unit 03020101 Nash NCDWR Region Raleigh Precipitation within 48 hrs? Latitude/Lonqitude (deci-deqrees) 35.989618/-77.903149 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.) • HabitaUplant 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 floodinq durinq 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 z 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. ❑<_ 15-feet wide ❑> 15-feet wide ❑ Other open water (no tributary present) 7d. Do roots of assessment area vegetation extend into the bank of the tributary/open water? ❑Yes ❑No 7e. Is stream or other open water sheltered or exposed? ❑Sheltered — adjacent open water with width < 2500 feet and no regular boat traffic. ❑Exposed — adjacent open water with width >_ 2500 feet or regular boat traffic. 8. Wetland Width at the Assessment Area — wetland type/wetland complex condition metric (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 ❑I ❑I ❑I From 0.1 to < 0.5 acre ❑J ❑J ❑J From 0.01 to < 0.1 acre ❑K ❑K ❑K < 0.01 acre or assessment area is clear-cut 12. Wetland Intactness — wetland type condition metric (evaluate for Pocosins only) ❑A Pocosin is the full extent (>_ 90%) of its natural landscape size. ❑B Pocosin type is < 90% of the full extent of its natural landscape size. 13. Connectivity to Other Natural Areas — landscape condition metric 13a. Check appropriate box(es) (a box may be checked in each column). Involves a GIS effort with field adjustment. This metric evaluates whether the wetland is well connected (Well) and/or loosely connected (Loosely) to the landscape patch, the contiguous naturally vegetated area and open water (if appropriate). Boundaries are formed by four-lane roads, 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. a 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 � ❑B ❑B Moderate density mid-story/sapling layer ��C �C Mid-story/sapling layer sparse or absent -� ❑A ❑A Dense shrub layer � ❑B ❑B Moderate density shrub layer ��C �C Shrub layer sparse or absent � ❑A ❑A Dense herb layer _ ❑B ❑B Moderate density herb layer �C �C Herb layer sparse or absent 18. Snags — wetland type condition metric (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 alt 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 NotA 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 � � � �,,,, f = ,-� r" �.�—... T -�. ,'� �.-.� , =�;� ;�� �v /'�',�'•�n.y�-�-.�;y,. . P", '�'',� z s � ., �j, ; • "� �i ,i a V � � �- � � � ,� , i '� r 4 c� ,�ry, r t�. � �,"� � l� _ ��;�� � �,��'+,� �, '� �.., � ,� i� 4'� ��- `_'� �\1:1''I J ° '� �r�', � .,.�f�"'S'� ` '�� �) � , � r(Ci •�.,.��: / y f: `•`..�_..`'"'�..'�� ����; •ti'_..� ��'!� 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 Assessment Area WE consists of riverine swamp forest bordered on the south and east by roads and private driveways and on the north and west by forested wetland. This assessment area is part of the Pig Basket Creek wetland system. A driveway was constructed through the wetland forming the east boundary and separating the assessment area from Wetland WD. Noticeable sheen on water surface. See photos in Attachment A. NC WAM Wetland Rating Sheet Accompanies User Manual Version 5.0 Wetland Site Name WE Date of Assessment 4/19/2018 Wetland Type Riverine Swamp Forest Assessor Name/Organization Sean Murray, VHB Notes on Field Assessment Form (Y/N) Presence of regulatory considerations (Y/N) 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) Assessment area experiences overbank flooding during normal rainfall conditions (Y/N) Assessment area is on a coastal island (Y/N) YES YES NO NO NO NO NO Sub-function Rating Summary Function Sub-function Metrics Rating Hydrology Surface Storage and Retention Condition MEDIUM Sub-surface Storage and Retention Condition MEDIUM Water Quality Pathogen Change Condition MEDIUM Condition/Opportunity MEDIUM Opportunity Presence (Y/N) NO Particulate Change Condition MEDIUM Condition/Opportunity MEDIUM Opportunity Presence (Y/N) NO Soluble Change Condition LOW Condition/Opportunity LOW Opportunity Presence (Y/N) NO Physical Change Condition LOW Condition/Opportunity LOW Opportunity Presence (Y/N) NO Pollution Change Condition NA Condition/Opportunity NA Opportunity Presence (Y/N) NA Habitat Physical Structure Condition MEDIUM Landscape Patch Structure Condition HIGH Vegetation Composition Condition HIGH Function Rating Summary Function Metrics Rating Hydrology Condition MEDIUM Water Quality Condition LOW Condition/Opportunity LOW Opportunity Presence (Y/N) NO Habitat Condition HIGH Overall Wetland Rating MEDIUM �� ,�' � 1 �= p ' � �` � �` , �� i � � � ,� � ��'�' � F�,; �?;�: ;.' � ` �.y� p(�p fi� �j r �'��f+'�1r9 h��' 'Y �i'e'� t{I ry�pL ]� � �� ��. . .� . � 1 � J�'. . �� ♦ ',-" � - 5I�-jfs`Y � ' �'S < ,�.�. .a �sc _ - r +ro A � `� '' r . 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