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HomeMy WebLinkAbout20181252 Ver 1_PJD Package_complete_20180913/ SlAff,;��\ i� � � .- ��T\-. I��� Y �. C� r I : pl. ,�"'s � a STATE OF NORTH CAROLINA DEPARTMENT OF T`RANSPORTATION ROY COOPER GOVERNOR September 12, 2018 Ms. Crystal Amschler U. S. Army Corps of Engineers NCDOT Regulatory Project Manager 151 Patton Avenue, Room 208 Asheville, NC 28801-2714 JAMES H. TROGDON, III SECRETARY Subject: PJD Request Package US 19/US 74/US 64/US 129 from end of divided section to SR 1556 (Martins Creek Road) Improvements UTs Hiwassee Lake, Cherokee County, NC TIP No. R-5735, State Project No. 50193.11 Dear Ms. Amschler: Please find attached the PJD request package. The original package was prepared in 2017, however, two project area enlargements and one correction to the JD package became necessary following final project design. Additional field investigations and changes to the package were made by the Division 14 Environmental Office to reflect the following: 1) The project area was enlarged to include a y-line connector road (Y3) extending about 300 feet from station 60+69 that will require temporary impacts (Site 3A, stream SA) to replace an existing length of 72" reinforced concrete pipe (RCP). 2) The project area was extended about 500 feet from station 91+15 to include, in part, a drainage outfall (Site 5, stream SA) west of Hiwassee Street at the east end of the proj ect. 3) Stream SC was not included in the original PJD package; however, it was listed as an impact by the designer and subsequently assessed as a jurisdictional feature on August 21, 2016. A DWR stream identification form for this stream is included in this revised package. 4) NCSAM forms were completed on all streams where permanent stream losses from culverts are proposed (Sites, 2, 3, and 4). NCSAM forms for these sites are included in the package. Please contact me at (828) 586-2141 if you have any questions or need additional information to evaluate this request. Mailing Addre.r.r: NC DEPARTMENT OF TRANSPORTATION Division 14 253 Webster Road Sylva, North Carolina 28779 Telephone:(828)586-2141 Fas: (828)586�043 Customer Service: 1-877-368-4968 Website: www.ncdot.Qov Location: NC DEPARTMENT OF TRANSPORTATION Division 14 253 Webster Road Sylva, North Carolina 28779 R-5735, PJD Package Page 2 September 12, 2018 `�`J'�3� bY' ����� 9/12/2018 86673FBE42E5415... Dave McHenry Division 14 Environmental Officer Enclosures: • PJD Forms Appendices 1 and 2 • Vicinity Map • Soil Maps • NWI Maps • USGS 7.5' Quad — Features Labeled • Waters of the U.S. on Aerial Photos — Features Labeled • Stream Quality Worksheets and DWR Stream ID Forms (ID Form for feature SC is located following NCSAM Results) • Wetland Forms and DWR Wetland Rating Sheets • NCSAM Results Appendix 1- REQUEST FOR CORPS JURISDICTIONAL DETERMINATION (JD) To: District Name Here • I am requesting a JD on property located at: us,s�us64�uS�4�us,2sf�omMan�nsc�eekRoadWeS�abo��,.2m��es (Street Address) City/Township/Parish: M��Pnv Coul�ty: cnerokee State: Nc Acreage of Parcel/Review Area for JD: 21 � Section: n�a Township: n�a Range: n�a Latitude (decimal degrees): 3s.o�sos3 Longitude (decimal degrees): -84.oaaoss (For linear projects, please include the center point of the proposed alignment.) • Please attach a survey/plat map and vicinity map identifying location and review area for the JD. • 01 currently own this property. _ I plan to purchase this property. 01 am an agent/consultant acting on behalf of the requestor. 0✓ Other (please explain): Ncoor o���s�on �a • Reason for request: (check as many as applicable) 01 intend to construct/develop a project or perform activities on this parcel which would be designed to avoid all aquatic resources. Q I intend to construct/develop a project or perform activities on this parcel which would be designed to avoid all jurisdictional aquatic resources under Corps authority. QI intend to construct/develop a project or perform activities on this parcel which may require authorization from the Corps, and the JD would be used to avoid and minimize impacts to jurisdictional aquatic resources and as an initial step in a future permitting process. Q✓ I intend to construct/develop a project or perform activities on this parcel which may require authorization from the Corps; this request is accompanied by my permit application and the JD is to be used in the permitting process. 01 intend to construct/develop a project or perform activities in a navigable water of the U.S. which is included on the district Section 10 list and/or is subject to the ebb and flow of the tide. DA Corps JD is required in order to obtain my local/state authorization. � I intend to contest jurisdiction over a particular aquatic resource and request the Corps confirm that jurisdiction does/does not exist over the aquatic resource on the parcel. 0 I believe that the site may be comprised entirely of dry land. 0 Other: • Type of determination being requested: 01 am requesting an approved JD. 01 am requesting a preliminary JD. � I am requesting a"no permit required" letter as I believe my proposed activity is not regulated. � I am unclear as to which JD I would like to request and require additional information to inform my decision. By signing below, you are indicating that you have the authority, or are acting as the duly authorized agent of a person or entity with such authority, to and do hereby grant Corps personnel right of entry to legally access the site if needed to perform the JD. Your signature shall be an affirmation that you possess the requisite property rights to request � J[�. or� the subject property. ocu igne by: � %�j����� 9/12/2018 *Signature: � `^ �""` �"�-- Date: • T�/p@CI Oi j�illlt@CI Il81118: Dave McHenry for Brian Burch, PE, NCDOT Division 14 Engineer COrppanynarpe: NCDOTDivision14 14CiC�i2SS: 253 Webster Road Sylva, NC 28779 �a�llll2 pi1011e I10.: $Z8�586-2141 ECllal� aC�(il"eSS: dgmchenry@ncdot.gov *Authorities: Rivers and Harbors Act, Section 10, 33 USC 403; Clean Water Act, Section 404, 33 USC 1344; Marine Protection, Research, and Sanctuaries Act, Section 103, 33 USC 1413; Regulatory Program of the U.S. Army Corps of Engineers; Final Rule for 33 CFR Parts 320-332. Principal Purpose: The information that you provide will be used in evaluating your request to determine whether there are any aquatic resources within the project area subject to federal jurisdiction under the regulatory authorities referenced above. Routine Uses: This information may be shared with the Department of Justice and other federal, state, and local government agencies, and the public, and may be made available as part of a public notice as required by federal law. Your name and property location where federal jurisdiction is to be determined will be included in the approved jurisdictional determination (AJD), which will be made available to the public on the DistricYs website and on the Headquarters USACE website. Disclosure: Submission of requested information is voluntary; however, if information is not provided, the request for an AJD cannot be evaluated nor can an AJD be issued. Appendix 2- PRELIMINARY JURISDICTIONAL DETERMINATION (PJD) FORM BACKGROUND INFORMATION A. REPORT COMPLETION DATE FOR PJD: g/� 2/� $ B. NAME AND ADDRESS OF PERSON REQUESTING PJD: Dave McHenry C. DISTRICT OFFICE, FILE NAME, AND NUMBER: �/IlfYlingtOn 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: Cil@rOk2@ c�ty: Murphy Center coordinates of site (lat/long in degree decimal format): �at.: 35.076063 �ong.: -84.044363 Universal Transverse Mercator: 16-769497.9, 3885474.9 Name of nearest waterbody: HIWaSSSee Lake E. REVIEW PERFORMED FOR SITE EVALUATION (CHECK ALL THAT APPLY): ❑� Office (Desk) Determination. Date: 9/12/18 ❑■ Field Determination. Date(s): 6/22/16, 8/21/18 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) Wq 35.073693 -84.040026 0.12 ac. PEM 1 Non-Section 10 Wetland S� 35.0739 —V4.0469 50 feet R5 Non-Section 10 Non-wetland S'/q 35.076467 -84.043484 450 feet R5 Non-Section 10 Non-wetland S' B 35.078683 -84.040015 50 feet R5 Non-Section 10 Non-wetland Wg 35.078720 -84.040026 0.003 ac. PEM 1 Non-Section 10 Wetland 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 applicanYs acceptance of the use of the PJD; (6) accepting a permit authorization (e.g., signing a proffered individual permit) or undertaking any activity in reliance on any form of Corps permit authorization based on a PJD constitutes agreement that all aquatic resources in the review area affected in any way by that activity will be treated as jurisdictional, and waives any challenge to such jurisdiction in any administrative or judicial compliance or enforcement action, or in any administrative appeal or in any Federal court; and (7) whether the applicant elects to use either an AJD or a PJD, the JD will be processed as soon as practicable. Further, an AJD, a proffered individual permit (and all terms and conditions contained therein), or individual permit denial can be administratively appealed pursuant to 33 C.F.R. Part 331. If, during an administrative appeal, it becomes appropriate to make an official determination whether geographic jurisdiction exists over aquatic resources in the review area, or to provide an official delineation of jurisdictional aquatic resources in the review area, the Corps will provide an AJD to accomplish that result, as soon as is practicable. This PJD finds that there "may be" waters of the U.S. and/or that there "may be" navigable waters of the U.S. on the subject review area, and identifies all aquatic features in the review area that could be affected by the proposed activity, based on the following information: SUPPORTING DATA. Data reviewed for PJD (check all that apply) Checked items should be included in subject file. Appropriately reference sources below where indicated for all checked items: �■ Maps, plans, plots or plat submitted by or on behalf of the PJD requestor: Map: � 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: Murphy 1:24k � Natural Resources Conservation Service Soil Survey. Citation: Cherokee County Soil Maps �■ National wetlands inventory map(s). Cite name: USFWS Wetland mapper � State/local wetland inventory map(s): � FEMA/FIRM maps: ❑ 100-year Floodplain Elevation is: .(National Geodetic Vertical Datum of 1929) �■ Photographs: �■ Aerial (Name & Date): NC One Map 2015 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: ���J� ^� 9/12/2018 �i� 86673FBE42E5415... Signature and 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. �. `. �, `�\ ," . ! " �'i`�Brr ,�c•, � Cheroke� ~ 4� ��. -- County � ;. ��'_ . . N� i� : �L n �` ''y �G�t "2" Begin Project • �" �. �¢�� Q,� :� - Legend Project Extent Roads County Boundary Streams & Lakes Municipal Boundary � Murphy �Rw��t� �� �i� iti��`�� ;a'�I���I`�►i � �-�r���j►�{��a r:i►�f�►��f � _•►�r~+ '��r��i ���`''�-�� �r�� .� � _ ys .t � �t �� �� 4� "� Murph.y � �l \ End Project � v i� ._ V _ AO �. _ _ -. kJi���il ' .�_' . � ' �„ �1� 4 = w�,�,��r �,, `' � a ,,, , , p k"5 , ,:i` `r,n MILES 0 0.25 0.5 1 1.5 2 �,�� NC DEPARTMENT OF TRANSPORTATION :; PROJECT DEVELOPMENTAND � ENVIRONMENTALANALYSIS UNIT US 19/US 74/US 64/US129 TO SR 1556 (MARTINS CREEK RD.) CHEROKEECOUNTY STIP PROJECT R-5735 � VICINITY MAP: FIGURE 1 s Key Map . :�.�L .. ,�• �our' - . � r �, � ` • , : � .� � � =� � .F � cy. & ; -� , � _ ., , �� `�� � � t� •� _� _ i, e . a '� � � _ t ` '`\ - 19/6� � . `i+�`�, ��� _� , �.' . . . . _ �' __ -, �QP���P �-'�: 'ir. � . � , � . � Y � _ ��� �" � I Begin Project ��r — �_�� � . -�� _ * �.y� �'� _, : •'.. ,;d - � � Study Area Boundary r„ y� 4 ' � County Boundary . ,��'' cHEROKEE Hydrologic Unit �� :�: - u� � � I �:. � - ���* .• � �. • � u ! � �,_ . - ' � • ,+� ��� ♦ �.� J� s . :@� �� � _ ,� ,� . ��,� � .. .�. �.�` � f � � � r � r � .i �' i� �. ,� �� " �� � - " � � � ��.� , � � � . �. _� NC D F-�it�=_� i C71=TRANSPORTATION County Soils Survey Map �� ~ Pk��ECi DtVELCPNIENTAND � r ��� �� -� ENVIRONMEN7ALANALYSISUNIT 'Xnv�E . �r�'' f Project No: R-5735 �/ _ US 19/U5 74/US 64/US129 WIDEN TO SR 1556 (MARTINS CREEK RD.) FEET = CHEROKEECOUNTY 0 100 200 400 {\ R_I 5735 STIP PROJECT R-5735 SOILS MAP: FIGURE 2 Y p �r � Ke M8 w �;herokee . �, , i., County _ w � 'fi • �' � �� � � � i } • •_ '� � .. 1 . . � ��. �. . . - '�' : - 19/64 v' .r = : -. _ v."s� ---_- . - � .a; � '� � � �1 . ' � r, �l' 1' .._.' � .. � ' � "� , �/�� , Y � � . ` � _ . �• Q • � r '�j . ; . � -,_'�' 1` . � , r � a w- �� Y,. � x�'N,C�� ������ � � -t`�` � , � �'` ,�;, � � ' , - ,� / , � j � -�,*a _ ; � `,�� v +: . . . .. , . ' i� �-_' End Project � r. • , . y � ' � - II�- , �Q� � ' . `� ��r IF" _, � � � � ,. �' , � F �r• � �� y� ��. .. � ; � � F� � A � � �^ •�� r}� ` •!- � � ' � _� t � . � � � - � p � , � �`='-�`J ,,'�� pROJECTDEVELOPME TAND,�TATION _--, � - � StudyArea Boundary County Soils Survey Map � r �- �r �� : ENVIRONMENTALANALYSISUNIT ,� �`�((4, ;---�-i Project No: R-5735 � Xn`�°E _ US 19/U5 74/US 64/US129 WIDEN �, y { � � I COUlItY BOUf1CJa1'y TO SR 1556 (MARTINS CREEK RD.) '=^�?r�� _ CHEROKEE COUNTY CHEROKEE HY(il'OIOgIC Unit FEET � �� STIP PROJECT R-5735 0 100 200 400 R-I 5735 SOILS MAP: FIGURE 3 Key Map r � � ' �� Fp\R4P�OR � � � �` � � 4 #` * 'V � � � i �� I � � � 7 �� f.� Cherokee, _ � ` �<°RqNG� """"'rw 4 � CoUnfy '�' ' � �' � RRO � �� � NpLIDAYpR � x ,�5� � �s `'� �� - IRy � � � � � l �� .� �_ �O � • � ' � J . _ � fi � � `� ♦ � O � . � � WA n ` - m ,� � �� �� + US �q �,- r, � 2 � � t ► •� .� "wY .,,� "'�:-�� � - � -a� � # �sis� y , s . v�►�'+� � � \ � � , � �, �i � �� ' � ��, � / - �, - r -� �� - � �, c �. u � ' �f' � � � t � r� �� � � ,��} � � � �'O �� � �� � . .`- . o� � � x �1- Begin Project � �► r �' �� � �� �+1 � �r � , } � � � r � � �� �Q.� � / � � . �'h �g � �� � �' /4 , � J� � �� � / � � �R � ' �r . • f r � 4 �� :�.. ���� aD�- ,1�,�&�9���jJa:��:�� �'c O ,�� . � � 1 .�� pROJECT DEVELOPMENTAND RTATIOP f20adWayS USGS 7.5 Topographic Quadrangle Map '� � ENVIRONMENTALANALYSISUNIT � „_.;.y'p � c:.:.c.'� I� 4 i �' ' Delineated WOUS h"'�'E� US 19/US 74/US 64/US129 WIDEN ✓�r� � �5�1) 1 inch equals 200 feet s' � Study Area Boundary TO SR 1556 (MARTINS CREEK RD.) FEET CHEROKEECOUNTY CHEROKEE � Count Boundar - -^` STIP PROJECT R-5735 L—_i y y 0 100 200 400 -"`'4 `� I R-5735 Hydrologic Unit WATERS OF U. S. MAP: FIGURE 6 Key Map �`p,RANGER,RD�— DEWEESEST � ,( � N J� ��FW p0/NT� � SA � � ���r � �R � -�r� " � , - r � �` . � � • - � � 9164 � - '' `� � � ''� � �S 6a H�� 1% . _ _••'} � � � � � -..� y ` �+r � r ` wg � ' � � � �� � • — '� '�.. se o �hero� ee y � � County � � � W � F� � z o � �� � � � � .�� � • ail�/� � � f / � + � '%' � — � � � SA } � y0 End Pro�ect � , i, �P � � � ' � ��Y y��� RO � r �\�y � ��No � � � �� � , ' � � G D� � � � m � a � � ° � `-' � • + k � � �1 - � � _�` � � R , � + �� � � � � � � � � � y . J � � � �_. � � Y �� � � ' o � �� a�. � � � � � � � � Z� _ � � �/w � J� Q � � 1 � Y. � r r y � � ,I . .:, � � � S r � � t; � � � � � � 1 • _ I =� �"" r '�� � � � l�°1'� �°� r-�- -- Y�- 5��3�7r18 0 o e ' , y � � � . � �/`^'`.��,, �.,�,. PROJECT DEVELOPMENTAND �TATIOP Roadways USGS 7.5 Topographic Quadrangle Map .,� _ ENVIRONMENTALANALYSISUNIT � C � r''0 ,�r� Delineated WOUS £" i ,,, �� ,� �, 9n,awe¢ US 19/US 74/US 64/US129 WIDEN I I���� "_ 1) 1 inch equals 200 feet � � s' � Study Area Boundary TO SR 1556 (MARTINS CREEK RD.) FEET CHEROKEECOUNTY CHEROKEE L__� County Boundary 0 100 200 400 '� ,� I R-5735 STIP PROJECT R-5735 � Hydrologic Unit WATERS OF U. S. 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A �r � :� ,' � a�" ' - � ��y r" b r . y�� ei " , � �jt'�A y � " }' *S S ��/�. � Sn¢• Iw �' ,1 � " �� � � . q � `r t. :: .�y v: � � ���. :y+_'✓a�v_ _ ` - �.._ a :t .�:T � ,,i �' - . �� .t pY� + Y� �*�;,� PROJECT DEVELOPMENTAND RTATIOP AI�II�I P�OIOgI�p� (�0��) M�p ���--��i��r��� - ENVIRONMENTALANALYSISUNIT hn`°"'E'� a � US 19/US 74/US 64/US129 WIDEN 1 inch equals 200 feet a�' � TO SR 1556 (MARTINS CREEK RD.) FEET CHEROKEECOUNTY 0 100 200 400 -�--�\ R-5735 STIP PROJECT R-5735 WATERS OF U. S. MAP: FIGURE 9 R-5735 Stream: S ,� NC DW Stream Identification Form Version 4.11 Date: �/����� / Pro)ecUSlte:US 19/74/64/129 Latitude:3s ���G yS « Evaluator. L J S f=: �, ' j County: Cherokee Longltude: -��� � y�5 7 G Total Points: Stream Determination (circle onej Other Stream is at �easr rnrermrrrenr `l� � Ephemeral Intermittent erenn F e.g. quad Name: M u r h if t 19 or oerennral rf t 30• � P Y A. Geomor holo (Subtotal =�� ) Absent Weak Moderate Strong 1° Continuity of channel bed and bank 0 1 2 � 2. Sinuosity of channel along thalweg 0 �1J 2 3 3. In-channel structure: ex. riffie-pool, step-pool, 0 1 � 3 ri le- ool seauence 4. Particle size oi stream substrate 0 1 2 ;3' � 5. Active/relict floodplain [0� 1 2 3 6. Depositional bars or benches 0 41 2 3 7. Recent alluvial deposits 0 1 2 8. Headcuts QJ 1 2 3 9. Grade control 0 0.5 C�1) 1.5 10. Natural valley 0 0.5 1.5 11. Second or greater order channel No = 0 Ye = 3J B. Hydrology (Subtotal = _! . .� ) 12. 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? 0 1 0 1 � � 0 0.5 0 0.5 No=O 2 � 2 0.5 0 1 1.� 1 1.5 : Yes Z3J C. Biolog Subtota! = I I ) 18. Fibrous roots in streambed (� 2 1 0 19. Rooted upland plants in streambed �2 1 0 20. Macrobenthos (note diversity and abundance) 0 �.� 1 2 3 21. Aquatic Mollusks �D ^ 1 2 3 22. Fish 0 0.5 � 1.5 23. Crayfish 0 0.5 1 �1.5� 24. Amphibians 0) 0.5 1 1.5 25. Algae 0 0.5 1 (1T 26. Wetland plants in streambed FACW = 0.75; OBL = 1.5 Other - 9 •perennial streams may also be identified using other methods. See p. 35 of manual. Notes: �, ; �'< .4�_ '�'^ � � �' - c�s �- Sketch: _ _ � _ - � �i v / � f--� `� y , c,nannei �uostrace: ciay / sut ��?�,gr�v�ev/ CObQ1e / dearocrc �cirae an cnac appiy� Water Velocity: fast / noderate� slow Water Clarity: cclea�'/ sfightly turbid / turbid . Water Depth: � � � �` inches � " Page1of20 I N T E R N AT I 0 N A L R-5735 USACE AiD# DWQ # Site # (indicate on attached map) Stream: S�_ „.�,; STREAM QUALITY ASSESSMENT WORKSHEET US 19/74/64/129 Pro�•ide the following information for the stream reach under assessment: 1. Applicant's name: NCDOT i 3. Date of evaluation:_� /d� �� G 5. Name of stream: !J ( N�-v c, s s<< ��� � i 7. Approximate drainage area: �3 a �4c r� s 9. Length of reach evaluated: /C�v -�� � 11. Site coordinates (if known): prefer in decimal degrees. Latitude (cx. 34.872312): _3 �� . 0? �O G`� 9' 2. Evaluator's name: �r� -= y� r, � 4. Time of evaluation: 3� G o:�`+ 6. River basin: Hiwassee 8. Stream order: 3�J � V%5 S�, .� Se. ,;� ,� � 10. Coun �� CherQkee 12. Subdivision name (if any): Longitude (ex. -77.SSiG11):_ � s `-1• 0 `� s' .5 % � Method location detennined (circle): PS. T�Shee17 Ortho (Aerial) Photo/GIS Other GIS Other 13. Location of reach under eva(uation (note near6y roads and landmarks and attach map identifying stream(s) location): _ N�U; 7rd�rs<<� .� o�" Y,7G; Ls D,��L �_ � K J Us 7�/ .� - — 14. Proposed channel work (ifany): v� �Hvw 15. Recent weather conditions: �� u�` � f' :, � 16. Site conditions at time of visit: ��-' y 17. Identify any special watenvay classifications known: _Section 10 �Tidal Waters _Essential Fisheries Nabitat __Trout Waters �Outstanding Resource Waters ` Nutrient Sensitive Waters _Water Supply Watershed (I-IV) 18. Is there a pond or lake located upstream of the evaluation point'? ES NO If yes, estimate the water surface area: o- 5�%+<• 19. Does channel appear on USGS quad n�ap? � NO 21. Estittiated watershed land use: � v% Residential �% Forested 20. Does channel appear on USDA Soil Survey'> � NO 1 U% Commercial f b% Industrial _% Agricultural �% Cleared! Logged % Other i , 22. Bankfull width: '� 23. Bank height (ti•om bed to top of bank): 3 24. Channel slope down center of stream: _Flat (0 to 2%) %� Gentle (2 to 4%) �Moderate (4 to 10%) �Steep (> ] 0%) 2S. Channel sinuosity: �Straight �Occasional bends _Frequent meander _Very sinuous _Braided channel Instructions for completion of worksheet (located on page 2): Begin by determining the most appropriate ecoregion based on location, terrain, vegetation, stream classification, etc. Every characteristic must be scored using the same ecoregion. Assign points to each characteristic within the range shown for the ecoregion. Page 3 provides a brief description of how to review the characteristics identitied in the worksheet. Scores should reflect an overall assessment of the stream reach under evaluation. If a characteristic cannot be evaluated due to site or weather conditions, enter 0 in the scoring box and provide an explanation in the comment section. Where there are obvious changes in the character of a stream under review (e.g., the stream flows from a pasture into a forest), the stream may be divided into smaller reaches that display more continuity, and a separate form used to evaluate each reach. Tl�e total score assigned to a stream reach must range between 0 and ] 00, with a score of 100 representing a stream of the highest quality. Total Score (from re�•erse): I�1 Comments: ,, . r- , E�•aluatoc's Signature ��� r % � �"='_- - Date :"r I �}�� . � This ehannel evaluation form is intedded to be used only as a guide to assist landowaers an�l environmental professionals in gat�ering the data required by the United States Army Corps of Esagineers to make a preliminary assessment of streem q�alih�. The tot�l score resulting from the completioe of this form is subject to USACE ap�proval and does not imply a particular mitigation ratio or requirement. Fomi subject to change — version OG/03. To Conunent, pl - - . . . 1 Page2of20 INTERNATIONAL r�p; R-5735 Stream: S fl STREAM QUALITY ASSESSMENT WORKSHEET US 19/74/64/129 # CHARACTERISTICS ECOREGION POINT RANGE SCORE i Coastal Piedmont Mountain Presence of flow / persistent pools io stream 1 (no �low or saturation = 0; stron flow = max points 0— 5 0— 4 0— 5 � 2 Evidence of past human alteration p_ 6 0— 5 0— 5 extensive alteration = 0; no alteration = max points � 3 Riparian zone 0— 6 0— 4 0— 5 (no buffer = 0• contiguous, wide buf%r = max oints 2 4 Evidence of nutrient or chemical dischar�es � 0— 5 0— 4 0— 4 (extensive discharaes = 0• no discharQes = max noints) � ,,,a Groundwater discbar�e � Q 5 no discharcte = 0� sarincts, see s wetlands etc. = max oints 0— 3 0— 4 0— 4 � 6 Preseece of adjaceot floodplain 0— 4 0— 4 0— 2 �„ (no floodplain = 0• extensive tlood lain = max points U a � Entreechmeet / floodplain access 0— 5 0— 4 0— 2 (dee�l entrenched = 0' frequent floodin = max noints � 8 Presence of adjacent wetlands 0— 6 0— 4 0— 2 (no wetlands = 0; larQe adiacent wetlands = max oints �.� 9 Channel sinuosity 0— S 0— 4 0— 3 � extensive channelization = 0; natural meander = max oints) 10 Sediment input 0— 5 0— 4 0— 4 .3 (extensive denosition= 0; little or no sediment = max noints 11 Siu & diversity of channel bed substrate NA* 0— 4 0— 5 3 fine, homoQenous = 0; larAe diverse sizes = max noints) 12 Evideoce of chaanel incision or wideninR 0— 5 0— 4 0— 5 a }� deenl incised = 0• stable bed & banks = max points) ,.E"„ Presence of major bank failures -_ � 13 0-5 0-5 0-5 _ �, severe erosion = 0� no erosion stable banks = max oints � 14 Root depth aod density on baoks 0— 3 0— 4 0— 5 3 F., no visible roots = 0; dense roots throuQhout = max points � Impact by aRriculture, livestock, or timber production 15 ' 0-5 0-4 0-5 ,� (substantial im act =0; no evidence = max points) 16 Presence of riffle-pool/ripple-pool compleaes 0— 3 0— 5 0— 6 `i E„� no riffles/ri les or ools = 0� well-develo�ed = max points) Q 1 � Ha6itat compleaity 0— 6 0— 6 0— 6 � � litde or no habitat = 0' frequent, varied habitats = max oints) � 1 g Canopy coverage over streambed 0— 5 0— 5 0— 5 j ,� no shadin veQetation = 0; continuous canop = max ooints) 19 Substrate embeddedness NA# 0— 4 0— 4 3 (deepl embedded = 0• loose structure = max � 20 Presence of stream invertebrates (see page 4) 0— 4 0— 5 0— 5 � � _ no evidence = 0• common. numerous tv es = max oints) (7 21 Presence of ampbibiaes 0— 4 0— 4 0— 4 O no evidence = 0; common, numerous tvnes = max points� U Presence of fis6 O 22 0-4 0-4 0-4 a � (no evidence = 0 common, numerous t pes = max points) _ 23 Evidence of wildlife use 0— 6 0— 5 0— S ! (no evidence = 0; abundant evidence = max points Total Points Possible 100 100 100 TOTAL SCORE (also enter on �rst page) `�' � * 1 hese character�st�cs are not assessed �n coastal streams. Page3of20 � INTERNATIONAL R-5735 Stream: S� NC DW Stream Identification Form Version 4,11 Date: �/�� ��� ProjecUSlte: US 19/74/64/129 Latitude: 3S Evaluator: ` County: Cherokee Longitude: - Total Points: Stream Determinat(on (cir��ne) Other Stream is at least intermittertt r.�� °� s Ephemeral Intermlttent t�erenn la e.g. quad Name: M u i/ 2 19 a oerennial i/ a 30' � �`� �---.-- A. Geomorphology (Subtotal =_,Lt S � 1° Continuity of channel bed and bank 2. Sinuosity of channel along thalweg 3. In-channel structure: ex. riffle-pool, step-pool, ripple-pc�l sequence 4. Particle size of stream substrate 5. Active/relict floodplain 6. Depositional bars or benches 7. Recent alluvial deposits 8. Headcuts 9. Grade control 10. Natural valley 11. Second or greater order channel artifrcial ditches are not rated; see discussions in manual Absent 0 0 0 0 0 0 0 �QI 0 0 No=O Weak 1 _ 1 1 1 1 �U 1 0.5 ff:i � Moderate Stroi 2 �. _�J 3 C?I 3 Q 3 2 3 3 2 3 2 3 � ]�j 1.5 1 1.5 Yes = 3� B. Hvdrolog Subtotal = I � ) 12. Presence of Baseflow 0 1 2 13. Iron oxidizing bacteria 0 1 2 i 14. Leaf litter 1.5) 1 0.5 0 15. Sediment on plants or debris 0 0.5� 1 1.5 16. Organic debris lines or piles 0 0.5 (]� 1.5 17. Soil-based evidence of high water table? No = 0 Ye�T3 C, Biolo Subtotal = 18. Fibrous roots in streambed 2 1 0 � 19. Rooted upland plants in streambed Q> 2 1 0 20. Macrobenthos (note diversity and a6undance) 0 1 2 3 21. Aquatic Mollusks 0 L1 2 3 22. Fish �0� 0.5 1 1.5 23. Crayfish �j 0.5 1 1.5 24. Amphibians 0 0.5 C1 1.5 25. Algae � 0.5 1 1.5 26. Wetland plants in streambed FACW =.75- BL = 1.5 Other = 0 'perennial streams may also be identified using other methods. See p. 35 of manual. Notes: � �.%�_:� �i,;�,�!�� � _ ad �J� f �.�, i,: _ . ��,f - - - - �� Sketch: ����v�`� �� . � ,- _ '� r ,, _t�l�, � l . t � ^r � i �/ y rl �� � 1 S �' o✓•. f„ �T_� 1 �. �.�"� __ � �� _ � v�. �Y S , Channel Substrate: clay / silt / 6and�/�gravgF/(cobble J bedrock (circle all that apply) Water Velocity: fast / moderate% slow Water Clarity: ��lear / slightly turbid / turbid Water Depth: � - G inches Page 4 Of 20 - . . I N T E R N A T I 0 N A L R-5735 USACE AID# DWQ # _ Site # (lI1dlCete nn attarhed manl Stream: S i-; ;,�,; STREAM QUALITY ASSESSMENT WORKSHEET - US 19/74/64/129 Pro�•ide the following information for the stream reach under assessment: 1. Applicant's name: NCDOT 3. Date of evaluation:_G/,,�ll �„ _ S. Name of stream: l.Ii �v �� i�,�/ c� S5 � c �,�v, s �u 12. Evaluator's name: ��te`' ��b9� r 4. Time of evaluation: �= .' �' CJ�r;-� 6. River basin: Hiwassee 7. Approximate drainage area: lS /4c r� � 8. Stream order: c� v, �% C�r,-,� `U /_ 9. Length of reach evaluated: I vG� �cc � 10. County: ('herokee 11. Site coordinaces (if known): prefer in decimal degrees. 12. Subdivision nan�e (if any): Catitude (cx. 34.872312): _� S. � 7 4S � U g Longitude (ex. -77.55661 I): '�'/ � U__� g% 7'3 _ Method location determined (cirde): �S �opo Sh�� Ortho (Aeria1) PhotoiGlS Other GIS Other 13. Location of reach under evaluation (note-near�iq-roads and landinark�and attach map identifying stream(s) location):_ _ � �,.�a�,;�� '�:,La.y,�. �. �e��,9� �'f" � �.� j" n�t�-��e � „ ,.,.t _ 14. Proposed channel work (if any): ' •_�.� , 1S. Recent weather conditions� i' c- ° t� � . 16. Site conditions at time of visit: 17. Identify any special waterway classifications known: _Section 10 _Tidal Waters _Essential Fisheries Habitat Trout Waters _Outstanding Resource Waters _ Nutrient Sensitive Waters _Water Supply Watershed (I-IV) 18. Is there a pond or lake located upstream of the evaluation point? YES �O�.If yes, estimate the water surface area: 19. Does channel appear on USGS quad map? YES � 21. Estimated watershed land use: �% Residential �% Forested 20. Dces channel appear on USDA Soil Survey? '�'S NO � % Commercial . S% [ndustrial _% Agricultural � % Cleared / Logged _% Other r 22. Bankfull width: S�c� �r 23. Bank height (1'rom bed ro top ofbank): ��` a� 24. Chacuiel slope down center of stream: _Flat (0 to 2%) �Gentle (2 to 4%) � Moderate (4 to 10%) _Steep (> 10%) 2S. Channel sinuosity: �Straight _Occasional bends __Frequent meander _Very sinuous _Braided channel Instructions for completion of worksheet (located on page 2): Begin by determining the most appropriate ecoregion based on location, terrain, vegetation, stream classification, etc. Every characteristic must be scored using the same ecoregion. Assign points to each characteristic within the range shown for the ecoregion. Page 3 provides a brief description of how to review the characteristics identiiied in the worksheet. Scores should reflect an overall assessment of' the strea�n reach under evaluation. If a characteristic cannot be evaluated due to site or weather conditions, enter 0 in the scoring box and provide an explanation in the comment section. Where there are obvious changes in the character of a stream under review (e.g., the stream Ilows from a pasture into a forest), the stream may be divided into smaller reaches that display more continuity, and a separate form used to evaluate each reach. The total score assigned to a stream reach must range between 0 and 100, with a score of 100 representing a stream of the highest quality. Total Score (from re�•erse): -S� _ Comments . ; � ' / , E�•alvator's Signaturee"�'� �' r/ ;'- e_�' Date E"- ',��� - This channel e��aluation form is inteoded to be used only as a guide to essist landowners and environmental professionals in gathering the data required by the United States Army Corps of Engineers to make � preliminary sssessment of stream quality. The total score resulting from the completion ot this form is subject to USACE approval sod does not im�ly a particular mitigation ratio or requirement� Form subject to cEiai�ge — versi�n 06/0�. To C€�mment, pl - - . . . I Page5ot20 INTERNATIONAL T�p; R-5735 Stream: � STREAM QUALITY ASSESSMENT WORKSHEET US 19/74/64/129 ECOREGION POINT RANGE # CHARACTERISTICS Coastal Piedmoot Mouotaio SCORE � Presence of tlow / persistent pools io stream 0— 5 0— 4 0— 5 (no flow or saturetion = 0; stron flow = max points =� Evidence of past 6uman alteration 2 extensive alteration = 0; no alteration = max oints 0— 6 0— 5 0— 5 � 3 Riparian zone 0— 6 0— 4 0— 5 a no buffer = 0• conti �ous, wide buffer = max ooints 4 Evideoce of nutrient or chemical dischar�es 0— 5 0— 4 0— 4 a (extensive discharaes = 0; no dischar es = max oints) ,,a Grouodwater discharge a U5 no dischar e= 0; sprin s seeps, wetlands etc. = max voints 0— 3 0— 4 0— 4 � Preseoce of adjaceot floodplaio � 6 no floodplain = 0 extensive flood lain = max oints) 0— 4 0— 4 0— 2 � a � Eotreochment / tloodplain access 0— 5 0— 4 0— 2 ' dee ]v entrenched = 0; fre uent floodinst = max points Preseoce of adjaceot wetlaods a 8 no wetlands = 0; larae adiacent wetlands = max oints 0— 6 0— 4 0— 2 9 Chaonel siouosity 0— 5 0— 4 0— 3 � (extensive channelization = 0; natural meander = max �ints) I 0 Sediment input 0— 5 0— 4 0— 4 a extensive deposition= 0; litde or no sediment = max �ints) 11 Siu & diversity of chanoel bed substrate NA• 0— 4 0— 5 Y fine, homoQenous = 0• lat e diverse sizes = max ooints) 12 Evidence of channel iocisioo or wideoiog 0— 5 0— 4 0— 5 `� �+ dee 1 incised = 0• stable bed & banks = max eints) ,,,E""„ Presence of major baok failures a 13 (severe erosion = 0; no erosion, stabie banks = max n�intsl 0— 5 0— 5 0— 5 3 � � 14 Root depth and deosity oo baoks 0— 3 0— 4 0— 5 3 �, no visible roots = 0• dense roots throu hout = max noints � Impact by agriculture, livestock, or timber productioo 15 (substantial im act =0• no evidence = max ooints) 0— 5 0— 4 0— 5 �, 16 Preseoce oi ritYle-pooUripple-pool compleaes 0— 3 0— 5 0— 6 F (no rit'fles/ri les or ools = 0• well-develo ed = max �oints d Habitat complexity �„F',� I� (little or no habitat = 0� fiequent, varied habitats = max vointsl 0— 6 0— 6 0— 6 � Caoopy coverage over streambed 18 0-5 0-5 0-5 (no shadin veaetation = 0' continuous canon = max noints) 19 I Su6strate embeddedness NA* 0— 4 0— 4 (dee I embedded = 0; loose structure = max) °� Preseoce of stream iovertebrates (see page 4) � 20 no evidence = Oz common, numerous 1vPes = max points) 0— 4 0— 5 0— 5 � V 21 Preseece of amphibians 0— 4 0— 4 0— 4 + O (no evidence = 0; common, numerous tvoes = max ointsl_ � 22 Presence of fish 0— 4 0— 4 0— 4 (� � no evidence = 0• common, numerous tv es = max points 23 Evideoce of wildlife use 0— 6 0— 5 0— 5 (no evidence = 0; abundant evidence = max �c�intsl Total Points Possible ] 00 100 100 TOTAL SCORE (also enter on first page) �� ' lhese charactenstics are not assessed m coastal streams. Page 6 of 20 I N T E R N A T I 0 N A L R-5735 Wetland: W � A WETLAND DETERMINATION DATA FORM — Eastern Mountains and Piedmont Pro)ecvsite: US 19L4L64�129 City�County: MUfphV� Cherokee Sampling Date: �( ��'�/G ApplicanVOwner: ,�/ G� O�_ State: _v L— Sampling Point: �"��' �✓ �'f Investigator(s): �ci ,Ssb�t; Section, Township, Range: __ _ Landform (hillslope, terrace, etc.): _!Jc �✓CSS r� Locat relief (concave, convex, none): _� a-,�.;,� C Slope (%): '< < i� Subregion (LRR or MLRA): S BIUe RIdQe Lat:,� 5• ��� � °� Long: ?5 %, C%`� ��'�� Datum: �-"C� S'�'. `/ Soi1 Map Unit Name; _U � � - � � � i �'�', � � � `S - CJ � S �. -. G �,.,W� NWI classification: �`�� �`' 1 Are climatic I hydrologic conditions on the site typical for this time of year9 Yes x No (If no, explain in Remarks.) Are Vegetation , Soil , or Hydrology significantly disturbed7 Are "Normal Circumstances" present? Yes x No Are Vegetation , Soil , or Hydrology naturally problematic? (If needed, explain any answers in Remarks.) SUMMARY OF FINDINGS — Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes '� No Hydric Soil Present? Yes �_ No Wetland Hydrology Present9 Yes '� No �� t o, , s :A..+ �`'' 1 irs �, � a r� c, ��'� J s � d G✓a ,� c C/ c c t�� HYDROLOGY Is the Sampled l4rea within a Wetland4 �S _ ,' . 0��,,.� Yes '� No � _�f Wetland Hydrology Indicators: Seconda,p� Indicators jminimum of rivo reguiredl Primarv Indicato�s fminimum of one is reauired: check all that a��lv) _ SuAace Soil Cracks (B6) Surface Water (A1) _ True Aquatic Plants (814) _ Sparsely Vegetated Concave SuAace (BS) X High Water Table (A2) _ Hydrogen Sulfide Odor (C1) � Drainage Pattems (B10) X Saturetion (A3) _ Oxidized Rhizospheres on Living Roots (C3) _ Moss Trim Lines (816) _ Water Marks (B1) _ Presence of Reduced Iron (C4) _ Dry-Season Water Table (C2) _ Sediment Deposits (82) _ Recent Iron Reduction in Tilled Soils (C6) _ Cra�sh Burrows (CB) _ Drift Oeposits (B3) _ Thin Muck Surface (C7) _ Saturation Visible on Aerial Imagery (C9) _ Algal Mat or Crust (84) _ Other (Explain in Remarks) _ Stunted or Stressed Plants (D1) _ Iron Deposits (B5) _ Geomorphic Position (D2) _ Inundation Visible on Aerial Imagery (87) _ Shallow Aquita�d (D3) _ Water-Stained Leaves (B9) _ Microtopographic Relief (D4) _ Aquatic Fauna (813) _ FAC-Neutrel Test (D5) Field Observations: Surface Water Present? Yes No X_ Depth (inches): Water Table Present9 Yes �c No Depth (inches): � ���y . c Saturation Present? Yes X No Depth (inches): S�� t°<< t Wetland Hydrology Present? Yes X No includes capillary frinae) Describe RPcorded Data (stream gauge, monitoring well, aerial photos, previous inspections), i( available: Remarks: - w� {'G � J �.` �'-_ _ _ �, , , '� � - Page 7 of 20 MICHAEL BAKER INTERNATIONAL US Army Corps of Engineers Eastem Mountains and Piedmont - Version 2.0 US 19/74/64/129 VEGETATION (Four Strataj - Use scientific names of plants. Abso�ute Dominant Indicator Tree Stratum (Plot size: ) % Cover S ecp ies? Status 1. _ 2. 3. _ _ 4. 5. 6. 7. 8. Saolino/Shrub Stratum (Plot size: � 5= ra;/ -,.� 6� 1. � i �� D c%i,:, c�,.--, "�cJ {n. �c •.•�-, 2. � a G L�'14 �, h! e 1.,+,• ,' p= e� '- 3. _�G /' x ��tc. 4. 5. 6. 7. 8. 9. 10. = Total Cover r o _�- F�� m v Y F.� c �.1l�� - `7' O � _ �� = Total Cover Herb stratum (P�ot size: S � ✓ • �' � �s � i..�.L��S C,�s��� 9v e�- �cw 2._�t.� sD. S N r`�,�c. r 3. 4. 5. 6. 7. 8. 9. 10. 11. 12. � �_= Total Cover Woody Vine Stratum (Plot size: � S� r��� �.�_ ) P -� (� 1. V� ',�-✓v w t,n�) � i' r 2. 3. 4. 5. 6. � = Total Cover emarks: (Include ,� or on a separate R-5735 Wetland: � Sampling Point: �-✓A • w c "f Dominance Test worksheet: 1Jumber of Dominant Species � That Are OBL, FACW, or FAC: (A) Total Number of Dominant Species Across All Strata: � (B) Percent of Dominant Species That Are OBL, FACW, or FAC: / v!�_ (A/g) Total % Cover of: Multiolv bv: OBL species x 1 = FACW species x 2 = FAC species x 3 = FACU species x 4 = UPL species x 5 = Column Totals: (A) (B) Prevalence Index = B/A = Hydrophytic Vegetation Indicators: _ 1- Rapid Test tor Hydrophytic Vegetation k 2- Dominance Test is >50°/a 3- Prevalence Index is 53.0� _ 4 - Morphological Adaptations' (Provide supporting data in Remarks or on a separate sheet) _ Problematic Hydrophytic Vegetation' (Explain) 'Indicators � hydric soil and wetland hydrology must be present, uNess disturbed or problematic. Definitions of Four Vegetation Strata: Tree - Woody plants, excluding vines, 3 in. (7.6 cm) or more in diameter at breast height (DBH), regardless o( height. Sapling/Shrub - Woody plants, excluding vines, less than 3 in. DBH and greater than 3.28 ft(1 m) tall. Herb - All herbaceous (non-woody) plants, regardless of size, and woody plants less than 3.28 R tall. Woody vine - All woody vines greater than 3.28 tt in height. Hydrophytic Vegetation Present? Yes � No US Army Corps of Engineers Eastem Mountains and Piedmont - Version 2.0 US 19/74/64/129 R-5735 Wetland: W A SO�L Sampling Point: ,C-,�s4- �✓r �r= Profile Description: (Describe to the depth needed to document the indicator or confirm the absence ot indicato�s.) Depth Matrix Redox Features „ inches Color (moist % �Color Imoist)" % Tvoe' Lce� Texture ,gemarks ��- � U ` i a �� 3 � � v _� � � � ;����_ � � _ ,� � �;�.,-� 'T : C=Concentration D=De Ip etion� RM=Reduced Matrix, MS=Masked Sand Grains. �Location: Pl=Pore Lining, M=Matrix. __ Hydric Soil Indicators: Indicators for Problematic Hydric Soils : Histosol (A1) _ Dark Surface (S7) _ 2 cm Muck (A10) (MLRA 147) Histic Epipedon (A2) _ Polyvalue Below Surface (S8) (MLRA 147, 148) _ Coast Prairie Redox (A16) B1ack Histic (A3) _ 7hin Dark Surface (S9) (MLRA 147, 148) (MLRA 147, 148) _ Hydrogen Sulfide (A4) _ Loamy Gleyed Matrix (F2) _ Piedmont Floodplain Soils (F19) Stratified Layers (A5) Depleted Matrix (F3) (MLRA 136, 147) _ 2 cm Muck (A10) (LRR N) 'K Redox Dark Surface (F6) � Depleted Below Dark Surtace (A11) _ Depleted Dark Surtace (F7) _ Very Shallow Dark Surface (TF12) Thick Dark Surface (Al2) _ Redox Depressions (F8) _ Other (Explain in Remarks) Sandy Mucky Mineral (S1) (LRR N, _ Iron-Manganese Masses (F12) (LRR N, MLRA 147, 148) MLRA 136) Sandy Gleyed Matrix (S4) _ Umbric Surface (F13) (MLRA 136, 122) 'Indicators of hydrophytic vegetabon and Sandy Redox (S5) _ Piedmont Floodplain Soils (F19) (MLRA 148) wetland hydrology must be present, Stripped Matrix (S6) Red Parent Material (F21) (MLRA 127, 147 unless disturbed or problematic. Restrictive Layer (if observed): Type: _ Depth (inches): Hydric Soil Present? Yes X No Remarks: '✓�� ` _�__ j�%(S(.-i'' G�✓C 'p yar� r.- l - 1�%lt+"r - } � .-�� ' 1 �, ( � � �C�-r ! f. I C C'�!:'' ?'�c� ' _ f, - s Page 9 0( 20 MICHAEL BAKER INTERNATIONAL US Army Corps of Engineers Eastem Mountains and Piedmont — Version 2.0 TIP: R-5735 Wetland: � WETLAND RATING WORKSHEET Fourth Version Project Name US 19/74/64/129 Nearest Road �LS 6`� County Cherokee Wetland area _v, <�, acres Wetland width _feet Name of evaluator �.� _ . - '� - � Date L /� � % / � Wetland location _ on pond or lake X on perennial stream w>' �' _ on intermittent stream _ within interstream divide other: Soil series: V r fS _ predominantly organic - humus, muck, or peat �C predominantly mineral - non-sandy _ predominantly sandy Hydraulic factors _ steep topography ditched or channelized total wetland width >_ 100 feet Adjacent land use (within '/� mile upstream, upslope, or radius) X forested/natural vegetation �S % 7� agriculture, urban/suburban �a % � impervious surface S % Dominant vegetation (1� �;cr�t,.a ��s✓S — ( 2 ) _G � � , a cJ � � �, . r, � , ., t � �--_. �3) Flooding and wetness semipermanently to permanently flooded or inundated seasonally flooded or inundated � intermittently flooded or temporary surface water _ no evidence of flooding or surface water Wetland type (select one)� Bottomland hardwood forest Pine savanna Headwater forest i Freshwater marsh Swamp forest Bog/fen s Wet flat � L� f =�`5� �� _ Ephemeral wetland � Pocosin Carolina bay _ Bog forest X Other: Nvr - ���° � 1 � The rating system cannot be applied to salt or brackish marshes or stream channels �ca�io� �� � _ . �..,_ „ , � ' .. � �! — ------------ — ---------- ---�.__•--..�---•-.. : R Water storage �. x 4.00 =� � A Bank/Shoreline stabilization C� x 4.00 = � �'�'etland rating T Pollutant removal '1 " x 5.00 = 50 I Wildlife habitat 2 x 2.00 = � �� � N Aquatic life value 3 x 4.00 = �� ! G Recreation/Education U x 1.00 = �� �** Add 1 point if in sensitive watershed and >! 0% nonpoint source disturbance wirh;n �/> n,;IP �� �rrPa,,,, ����I�n; or radius Page10of20 I N T E R N A T I 0 N A L R-5735 Wetland: W A- cJ�-'i�K� WETLAND DETERMINATION DATA FORM — Eastern Mountains and Piedmont ProjectlSite: US 19/74/64/129 City/County: MU�ghV/ Cherokee Sampling Date: '%f����� ApplicanUOwner: N� AC r State: 'i%� . Sampling Point: �-� Investigator(s): � �', =� :��� Section, Township, Range: Landtorm (hillslope, terrace, etc.): h� ��<<%u� c Local reliei (concave, convex, none): t:�✓c �C Slope (�): �/0 9�, Subregion (LRR or MLRA): S BIU2 RIdg2 Lat: _ � � � � � g �� Long: _� �i `�. C� y '; � � �=- Datum:.�''�`F> ' Soil Map Unit Name: _ i% f� ' Uc'D r �;�� �.�, '� �° l�,�` .� ?�� r, �J NWI classification: � r_/ j',� r:- r � Are climatic / hydrologic conditions on fhe site typical for this time of year9 Yes �_ No (Ii no, explain in Remarks.) Are Vegetation , Soil , or Hydrology significantly disturbed9 Are 'Normal Circumstances" present9 Yes � No Are Vegetation _� Soil , or Hydrology naturally problematic9 (If needed, explain any answers in Remarks.) SUMMARY OF FINDINGS — Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present7 Yes Hydric Soil Present9 Yes Wetland Hydrology Present� Yes �r�h '� HYDROLOGY No � No No � Is the Sampled Area within a WeHand7 ���, - �r 4, , Yes No � i Wetland Hydrology Indicators: Secondarv Indicators (minimum of lwo reauired] Primarv Indicatons_ImLimum of one is_reauired: check all that aoolvl _ Sur(ace Soil Cracks (B6) Surface Water (A1) _ True Aquatic Plants (B14) _ Sparsely Vegetated Concave Surface (B8) _ High Water Table (A2) _ Hydrogen Sulfide Odor (C1) _ Drainage Patterns (B10) Saturation (A3) _ Oxidized Rhizospheres on Living Roots (C3) _ Moss Trim Lines (816) Water Marke (B1) _ Presence of Reduced Iron (C4) _ Dry-Season Water Table (C2) Sediment Oeposits (82) _ Recent Iron Reduction in Tilled Soils (C6) _ Cray(ish Burrows (CS) Drift Deposits (B3) _ Thin Muck SuAace (C7) _ Saturation Visible on Aerial Imagery (C9) Algal Mat or Crust (84) _ Other (Explain in Remarfcs) _ Stunted or Stressed Plants (01) Iron Deposits (BS) _ Geomorphic Position (D2) Inundation Visible on Aerial Imagery (67) _ Shallow Aquitard (D3) Water-Stained Leaves (B9) _ Microtopographic Relief (D4) _ Aquatic Fauna (B13) _ FAC-Neutral Test (DS) Field Observations: SuAace Water Present9 Yes No X Depth (inches): Water Table Present? Yes No 1r Depth (inches): _�.� U"� Saturation Present9 Yes No ?C Depth (inches): _�� d Wet�and Hydrology Present? Yes No X includes ca illa frinae Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: Remarks: r 1 ��' r;1,:1/��, 1 � ,),.�'-i �G,.r;G� �. ` - ,' , ,"�' �/�S� r� � . Page II of 20 MICMAEL BAKER INTERNATIONAL US Army Corps of Engineers Eastem Mountains and Piedmont — Version 2.0 US 19/74/64/129 VEGETATlON (Four Strata) - Use scientific names of plants. Absotute Dominant Indicator Tree Stratum (Plot size: ) % Cover S�ecies� Status ,. 2. 3. 4. 5. 6. 7. 8. = Total Cover Saolina/Shrub Stratum (Plot size: % �' � ""��'L� ) �. Qr�n�,5 c��-� { �,, „ � .4at� 2. �e+ •, � � ��r_'s� `�p �f � cl 3. ��c�cv� FGlca c, Y ��CsJ 4. - ; �' � . .� -f J � E" c � `� G. S. I�U S / r,1�0. ���i�, __ �� � 1��l�`C/ 6. � 7. 8. 9. 10. � _� = Total Cover Herb Stratum (Plot size: S'�' �i�� i5 ) 1. N � C ✓ ! � 'v m A N �, i� � � ,. ni- �.1� �_ ! 2.,�G` i1 t v`�_ c, r d�c., -�- `'i vLit_ 3. 4. 5. 6. 7. 8. 9. 10. 11. 12. R-5735 Wetland: W �1- ✓�/a k,J Sampling Point: WA-UP Oominance Test worksheet: Number of Dominant Species That Are OBL, FACW, or FAC: Total Number oi Dominant Species Across All Strata: Percent of Dominant Species That Are OBL, FACW, or FAC Index worksheet: -.�.� caB) Total �o C�ver ot: Multiolv bv: OBL species x 1 = , FACW species x 2 = FAC species _1,j=_ x 3 = . ''�.S FACU species y i�, x 4= / 15 � UPL species _,�, x 5= c� .� Column Totals � � (A) �� V (B) Prevalence Index = B/A = �_� Hydrophytic Vegetation Indicators: _ 1- Rapid Test for Hydrophytic Vegetation 2 - Dominance Test is >50% 3- Prevalence Index is 53.0' _ 4 - Morphological Adaptations' (Provide supporting data in Remarks or on a separate sheet) _ Problematic Hydrophytic Vegetation' (Explain) 'Indicators of hydric soil and wetland hydrotogy must be present, unless disturbed or problematic. Definitions of Four Vegetation Strata: Tree - Woody plants, exciuding vines, 3 in. (7.6 cm) or more in diameter at breast height (DBH), regardless of height. SaplinglShrub - Woody plants, excluding vines, less than 3 in. DBH and greater than 3.28 ft(1 m) tall. Herb - All herbaceous (non-woody) plants, regardless of size, and woody plants less than 328 ft tall. Total Cover Woody vine - All woody vines greater than 3.28 ft in ' �-1�- height. Woodv Vine Stratum (Plot size: � E -� f• r� �� ) ! � �r' 1._��� C�."',�c^:��yC� �'��� -_�`.�. '�` - . 2. 3. 4. 5. 6. or on a separate �:� � � �-_ � ,.-; a US Army Corps of Engineers Page 12 ot 20 ,_,`�_, = Total Cover r°:'�,,�- Q%i�c�7 � , Hydrophytic Vegetation y Present? Yes No �� Eastem Mountains and Piedmont - Version 2.0 US 19/74/64/129 R-5735 Wetland: W - v 14., SOiL Sampling Poinh --�+E� c�. Profile Description: (Describe to the depth needed to dceument the indicator or confirm the absence of indicators.) Depth Matrix Redox Features ,(inchesl_ Color moi t�` �o Color moist °k Tvoe Loc Teactur� Remarks i C)'dv `' _�R+ '� 6 _�:�Y''}- 'T : C=Concentration, D=De letion, RM=Reduced Matrix MS=Masked Sand Grains. �Location: Pl=Pore Linin , M=Matrix. Hydric Soil Indicators: Indicators tor Problematic Hydric Soils7: Histosol (A1) _ Dark Surface (S7) _ 2 cm Muck (A10) (MLRA 147) Histic Epipedon (A2) _ Polyvalue Below SuAace (S8) (MLRA 147, 148) _ Coast Prairie Redox (A16) Black Histic (A3) _ Thin Dark Surtace (S9) (MLRA 147, 148) (MLRA 147, 148) _ Hydrogen Sulfide (A4) _ Loamy Gleyed Matrix (F2) _ Piedmont Floodplain Soils (F19) Stratified Layers (A5) _ Depleted Matrix (F3) (MLRA 136, 147) 2 cm Muck (A10) (LRR N) _ Redox Dark Surface (F6) _ _ Depleted Below Dark Surface (A11) _ Depleted Dark Surtace (F7) _ Very Shallow Dark Surtace (TF12) Thick Dar1c SuAace (Al2) _ Redox Depressions (F8) _ Other (Explain in Remarks) _ Sandy Mucky Mineral (S1) (LRR N, _ Iron-Manganese Masses (F12) (LRR N, MLRA 147, 148) MLRA 136) Sandy Gleyed Matrix (S4) _ Umbric Surtace (F13) (MLRA 136, 122) 'lndicators of hydrophytic vegetation and Sandy Redox (S5) _ Piedmont Floodplain Soils (F19) (MLRA 148) wetland hydrology must be present, Stripped Matrix (S6) Red Parent Material (F21) (MLRA 127, 147 unless disturbed or problematic. Restrictive Layer (it observed): Type: Depth (inches): Hydric Soil Present? Yes No k I Remarks: �_1 1 - l '� ✓ - .� '� c tr, � U � �� ;., , ;� � � . , � � ��% :��: Page 13 ot20 MICHAEL BAKER INTERNATIONAL US Army Corps of Engineers Eastern Mountains and Piedmont — Version 2.0 R-5735 Wetland: � WETLAND DETERMINATION DATA FORM — Eastern Mountains and Piedmont ProjecuSite: US 19/74/64/1Z9 City/County: MUfpI1� Cherokee Sampling Date: G� ��, !�� Applicant/Owner. �?�C t' � 5tate:� Sampling Point:_'`-:.^1? ��c ` Investigator(s): �� ��ry �� � _ Section, Township, Range: Landform (hillslope, terrace, eta): f�o o J i Ili , h Local relief (concave, convex, none): _C o n, c. � t Slope (%): i lC 9 n Subregion (LRR or MLRA): S BiUe Rld�� Lat 3� D%� G U� Long: -�S `�� �'� -S �� �� Oatum: '+�G S$` Soil Map Unit Name: � v Vl � � V 5�o, ' f.gF �, �G�.,r' l:_ Y _ NWI classification: PFU I� P< �' L _ Are climatic / hydrologic conditions on the site typical for this time of yearl Yes � No (Ii no, explain in Remarks.) Are Vegetation __, Soil , or Hydrology significantly disturbed� Are "Normal Circumstances" present? Yes `� No Are Vegetation __, Soil , or Hydrology naturally problematic9 (If needed, explain any answers in Remarks.) SUMMARY OF FINDINGS — Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic VegetaGon Present9 Yes k No Hydric Soil Present� Yes Y No Wetland Hydrology Present� Yes i� No Remarks: � rc � � c� _�m�.+ 1� ��,; *� l�9.�,��� HYDROLOGY Is the Sampled Area within a Wetland? . 5 f r r a,,., ,SQ Yes � No Wetland Hydrology Indicators: Secondarv Indicators fminimum of two reauired� Primarv lndicators fminimum of one is reauired: check � that aoolvl _ Surface Soil Cracks (B6) SuAace Water (A1) _ True Aquatic Plants (814) _ Sparsely Vegetated Concave Surface (B8) �' High Water Table (A2j _ Hydrogen Sulfide Odor (C1) �[ Drainage Pattems (B10) ,�C Saturation (A3) _ Oxidized Rhizospheres on Living Roots (C3) _ Moss Trim Lines (816) Water Marks (B1) _ Presence oi Reduced Iron (C4) _ Dry-Season Water Table (C2) Sediment Deposits (B2) _ Recent Iron Reduction in Tilled Soils (C6) _ Creyfish Burrows (C8) Drift Deposits (B3) _ Thin Muck Surface (C7) _ Saturation Visible on Aerial Imagery (C9) Algal Mat or Crust (B4) _ Other (Explain in Remarks) Stunted or Stressed P{ants (D1) Iron Deposits (85) � Geomorphic Position (D2) I Inundation Visible on Aerial Imagery (B7) _ Shallow Aquitard (D3) Water-Stained Leaves (B9) _ Microtopographic Relief (D4) _ Aquatic Fauna (813) _ FAC-Neutral Test (D5) Field Observations: Surface Water Present? Yes No � Depih (inches): Water Table Present9 Yes � No __ Depth (inches): , ���c. c r Saturation Present? Yes �_ No Depth (inches): _ ti v� Fa << Wetland Hydrology Presentl Yes �i' No (includes capillary frinpe) Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: Remarks: r wci�c,H� �1yJ��'��ar. �� �1�;s �,n ,,: � �- ,, PegE 14 Of ZO MIGHAEI EIAKER INT ERNA1 IONAL US Army Corps of Engineers Easlem Mountains and Piedmont - Version 2.0 US 19/74/64/129 VEGETATION (Four Strata) - Use scientific names of plants. Absolute Dominant Indicator Tree Stretum (Plot size: ,�S �' �ud� ✓S ) % Cover Soecies7 Status 1. i., �; G�c7�m.sJ sa -, '/�I. ,� ic, - � �,n:: 2 C�c,� �_�[.�c, Cc.d �n��,�t� ��-�AL 3. 4. 5. 6. 7. 8. '� C� = Total Cover �e ir glShrub Stratum (Plot size: ) 1. 2. 3. 4. 5. 6. 7. - 8. 9. 10. , = Total Cover Herh Stratum (Plot size: 3 � ✓QJ�L�_ ) �. J�n�v� c�'�'.,s�s �� Y L�tw 2. T.ti,nu'�''i�� S ;g �.,�: a� � r-� � 3. 4. 5. 6. 7. 8. 9. 10. 11. 12. _j � = Total Cover Woodv Vine Stratum (Plot size: ) 1. 2. 3. 4. 5. 6. = Total Cover >marks: (Include photo numbers here or on a separate sheet.) ` �:. � ,�- ..�� ., � -. � R-5735 Wetland: W %3 Sampling Point: �� Dominance Test worksheet: Number of Dominant Species That Are OBL, FACW, or FAC: �(q) Total Number of Dominant �/ Species Across All Strata: / (B) Percent of Dominant Species That Are OBL, FACW, or FAC: / U(� (A/8) Total % Cover of: Multiplv bv: OBL species x 1 = FACW species _ x 2 = FAC species x 3 = FACU species x 4 = UPL species x 5 = Column Totals: (A) (B) Prevalence Index = B/A = Hydrophytic Vegetation Indicators: _ 1- Rapid Test for Hydrophytic Vegetation � 2 - Dominance Test is >50% 3- Prevalence Index is 53.0' _ 4 - Morphological Adaptations' (Provide suppoRing data in Remarks or on a separate sheet) _ Problematic Hydrophytic Vegetation' (Explain) 'Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. Definitions of Four Vegetation Strata: Tree - Woody plants, excluding vines, 3 in. (7.6 cm) or more in diameter at breast height (DBH), regardless of height. Sapling/Shrub - Woody plants, excluding vines, less than 3 in. DBH and greater than 3.28 R(1 m) tall. Herb - All herbaceous (non-woody) plants, regardless of size, and woody plants less than 3.28 R tall. Woody vine - All woody vines greater than 3.28 ft in height. Hydrophytic Vegetation Present7 Yes � No � 1 5 of �0 Ta BA N �I fTZSAA� US Army Corps of Engineers Eastem Mountains and Piedmont - Version 2.0 U S 19/74/64/129 R-5735 Wetland: W �? SOIL Sampling Point: ,�,1 n, � �:."_-'� Pro(ile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators,) Depth Matrix Redox Features i c s� Color moist % Color (moist) °6 Tvoe Loc� Texture Remarks C� �o ' ' _L /� l 3 l / � v !v /Z ]�— �� �.� -� [ a4 � � 'T� : C=Concentration D=Oepletion, RM=Reduced Matrix, MS=Masked Sand Grains. 'Location: PL=Pore Lining, M=Matrix. Hydric Soil Indicators: Indicators for Problematic Hydric Soils : Histosol (A1) _ Dark Surface (S7) _ 2 cm Muck (A10) (MLRA 147) Histic Epipedon (A2) _ Polyvalue Below Surface (S8) (MLRA 147, 148) _ Coast Prairie Redox (A16) Black Histic (A3) _ Thin Dark Surface (S9) (MLRA 147, 148) (MLRA 147, 148) _ Hydrogen Sulfide (A4) _ Loamy Gleyed Matrix (F2) _ Piedmont Floodplain Soils (F19) Stratified Layers (AS) Depleted Matrix (F3) (MLRA 136, 147) 2 cm Muck (A10) (LRR N) � Redox Dark Surface (F6) _ Oepleted Below Dark Surface (A11) _ Depleted Dark Surface (F7) _ Very Shallow Dark Surface (TF12) Thick Dark Surtace (Al2) _ Redox Depressions (F8) _ Other (Explain in Remarks) Sandy Mucky Mineral (S1) (LRR N, _ Iron-Manganese Masses (F12) (LRR N, MLRA 147, 148) MLRA 136) Sandy Gleyed Matrix (S4) _ Umbric Surface (F13) (MLRA 136, 122) 3lndicators of hydrophytic vegetation and Sandy Redox (SS) _ Piedmont Floodplain Soils (F19) (MLRA 148) wetland hydrology must be present, Stripped Matrix (S6) Red Parent Material (F21) (MLRA 127, 147) unless disturbed or problematic. Restrictive Layer (i( observed): Type: Depth (inches): Hydric Soil Present? Yes � No Remarks� �� � � y , � � � �r ::� , l o �.. d- �; , � ,I� ' `v'`v� ��?,� j � Y�,/ � G !� G � C-Cu �vi�� Page 16d20 MICHAEL BAKER INTERNATIONAL US Army Corps of Engineers Eastem Mountains and Piedmont — Version 2.0 R-5735 Wetland: W_- �- WETLAND DETERMINATION DATA FORM — Eastern Mountains and Piedmont u P!� Pro�ecus�te: US 19/74/64/129 CitylCounty: MUfpF1VI Cherokee samPi�n9 �ate: ���a �/ � ApplfcanVOwner: /�✓G/�G% State: _.fJ� Sampling Point: �� Investigator(s): `� -� .�6�sA ��°' Section, Township, Range: Landform (hillslope, terrace, etc.): � ' � �v [' . Local relief (concave, convex, none): _� a� U � �' Slope (°k): � ���J_ p Subregion (LRRorMLRA): 5 BIU2 RICJ�2 Lat:_3 .5, D �r4 ;.�' '� Long: — fr �r; =.�4'��'�S Datum:_''�'GS &�/ Soil Map Unit Name: .� V h A � V� c, - j� � �;: ��' t,< NWI classification: U�l�` `'/ f Are climatic I hydrologic conditions on the site typical for this time of year9 Yes � No (I( no, explain in Remarks.) Are Vegetation , Soil , or Hydrology significantly disturbed? Are 'Normal Circumstances' present9 Yes � No Are Vegetation __, Soil , or Hydrology naturally problematic9 (If needed, explain any answers in Remarks.) SUMMARY OF FINDINGS — Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present7 Yes Hydric Soil Present� Yes Wetland Hydrology Present9 Yes r ic�, n ! ' � (,.J A� (G� n � 0 HYDROLOGY No � �s the Sampled Area No X Within a Wetland? No k � Yes No � Wetland Hydrology Indlcators: Secondarv lndicators (minimum of two reQuired) Primar�t Indicato�5 lminimumof one is reauired� check all that ao Ivl _ SuAace Soil Cracks (86) SuAace Water (A1) _ True Aquatic Plants (B14) _ Sparsely Vegetated Concave SuAace (88) High Water Table (A2) _ Hydrogen Sulfide Odor (C1) _ Orainage Patterns (810) Saturation (A3) _ Oxidized Rhizospheres on Living Roots (C3) _ Moss Trim Lines (816) Water Marks (B1) _ Presence of Reduced Iron (C4) _ Dry-Season Water Table (C2) Sediment Deposits (B2) _ Recent Iron Reduction in Tilled Soils (C6) _ Crayhsh BuRows (C8) Drift Deposits (83) _ Thin Muck Surface (C7) _ Saturation Visible on Aerial Imagery (C9) , Algal Mat or Crust (84) _ Other (Explain in Remarks) _ 5tunted or Stressed Plants (D1) Iron Deposits (B5) _ Geomorphic Position (D2) Inundation Visible on Aerial Imagery (B7) _ Shallow Aquitard (D3) Water-Stained Leaves (B9) _ Microtopographic Retief (D4) _ Aquatic Fauna (813) _ FAC-Neutral Test (D5) Field Observations: Surface Water Present9 Yes No � Depth (inches): Water Table Present9 Yes No �C_ Depth (inches): 7 c�o ' Saturation Present� Yes No�_ Depth (inches): %r�a �� Wetland Hydrology Present? Yes No �' (includes ca illa frin e � Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: Remarks: v� c � � �. � ;� Gr� �J ru ( o � � i s f�o �� ,:' .�' ��:; C - � 7� Paae 17 of 2o MICHAEL BAKER INTERNATIONAL US Army Corps of Engineers Eastem Mountains and Piedmont - Version 2.0 US 19/74/64/129 VEGETATION (Four Strata) - Use scientific names of plants. Absolute Dominant Indicator Tree Stratum (Plot size: �d �) % Cover S e i t t s 1. f� (� � ! v S r a•h ��_ �/ r{ c. 2. s°�5 f�or��da � � ��cv 3. ��� u rs s S C ��.l, .,, c, -�_ �_F�i c✓ 4. _�. `1�:.1��Gb,i2:L.� ' �G _Z.�� � i4 G t/ 5. _P �� v 5 r i` g i d a G,� 5-- _�_ � G fJ 6. 7. 8. , %S� =TotalCover Saalina/Shrub Stratum (Plot size: P 4 �` = �° - � ) 1. .L � �1c �Qc, � � � ( ��'"C_. ci 2. C v� n v5 n� ;:'' e, _�- y ��;�J s. SasSGF.�,�, Q/6;�!v�-., � 4' rkL✓ 4. �i1 v c � c „� � . / ; .;, .j� �- ��4 L V 5. 6. 7. 8. 9. 10. � e� �_ = Total Cover Herb Stratum (Plot size: � ' '`�'�' "� ) � 1. , t x n ..�.� °� r'` d r C, - - �'� r f� �. � � 2.,������li'�c'_+'c?S�icl� ✓� � r�C(/ 3. �r'�. ,9f�r:< /Yya�'' � � ��.� r_ ^LCJ a 4. 5. 6. 7. 8. 9. 10. 11. 12. R-5735 Wetland: W - B vpiuti� Sampting Point: �� Test worksheet: Number of Dominant Species That Are OBL, FACW, or FAC: �(A) Total Number o( Dominant Species Across All Strata: 1'� (B) Percent ot Dominant Species That Are OBL, FACW, or FAC: ��_ (A/B) Total % Cover of� Multi�lY by: OBL species x 1 = FACW species -� x 2 = FAC species -� x 3= 7 S FACU species �.s x 4= 3 Q UPL species x 5 = Column Totals: � a v (A) `-� $.S_ (B) Prevalence Index = B/A = 5� O _ 1- Rapid Test (or Hydrophytic Vegetation 2 - Dominance Test is �50% 3- Prevalence Index is s3.0' _ 4 - Morphological Adaptations' (Provide supporSing data in Remarks or on a separate sheet) _ Problematic Hydrophytic Vegetation' (Explain) 'Indicators oi hydric soil and wetland hydrology must be present, unless disturhed or problematic. Detinitions of Four Vegetation Strata: Tree - Woody plants, excluding vines, 3 in. (7.6 cm) or more in diameter at breast height (DBH), regardless of height. Sapling/Shrub - Woody plants, excluding vines, less than 3 in. DBH and greater than 3.28 ft(1 m) tall. Herb - All herbaceous (non-woody) plants, regardless of size, and woody plants less than 3.28 ft tall. � o��„ = Total Cover Woo�dy vine - All woody vines greater than 3.28 ft in �y Vine Stratum (Plot size: ' � � f �' �'�' � ) 9 i `ef G L T�"?�' C�+�7� �,��-,-�I��(4H5 � � z_-pa�yl�c.,oc�ssvs �lur'nc[�c�u',�^„����_�� r�'Cv 3. 4. 5. 6. � (� = Total Cover Remarks: (Include photo numbers here or on a separate sheet.) �y �.�e�s;� � f ,� � � �, r �, - , , :-�.� � , ; Gv Page 18 of 20 '- US Army Corps of Engineers Hydrophytic Vegetation Present? Yes No � Eastem Mountains and Piedmont - Version 2.0 US 19/74/64/129 R-5735 Wetland: W (�un���J 501L Sampling Point: J _ c��„ Profile Oescription: (Oescribe to the depth needed to document the indicator or confirm the absence of indicatorsJ Depth Matrix Redox Features (inchesl Color (moisU % Color fmoist) 96 Tvne Loc Texture Remarks (��o)D / ` �, � �'� �� li/ lGO � s: „i � rc ., - 'T e: C=Concentration D=De letion, RM=Reduced Matrix MS=Masked Sand Grains. 2Location: PL=Pore Linin , M=Matrix. Hydric Soil Indicators: Indicators Ior Problematic Hydric Soils : Histosol (A1) _ Oark Surtace (S7) _ 2 cm Muck (A10) (MLRA 147) Histic Epipedon (A2) _ Polyvalue Below Surface (S8) (MLRA 147, 148) _ Coast Prairie Redox (A16) Black Histic (A3) _ Thin Dark Surface (S9) (MLRA 147, 148) (MLRA 147, 148) Hydrogen Sulfide (A4) _ Loamy Gleyed Matrix (F2) _ Piedmont Floodplain Soils (F19) Stratified Layers (A5) _ Depleted Matrix (F3) (MLRA 136, 147) 2 cm Muck (A10) (LRR N) _ Redox Daric Surface (F6) _ Depleted Below Dark Surface (A11) _ Depleted Dark Surface (F7) _ Very Shatlow Dark Surtace (TF12) Thick Dark Surface (Al2) _ Redox Depressions (F8) _ Other (Explain in Remarks) _ Sandy Mucky Mineral (S1 j(LRR N, _ Iron-Manganese Masses (F12) (LRR N, MLRA 147, 148) MLRA 136) Sandy Gleyed Matrix (S4) _ Umbric Surface (F13) {MLRA 136, 122) 'Indicators of hydrophytic vegetation and Sandy Redox (S5) _ Piedmont Floodplain Soils (F19) (MLRA 148) wetland hydrology must be present, Stripped Matrix (S6) Red Parent Material (F21) (MLRA 127, 147) unless disturbed or problematic. Restrictive Layer (if observed): Type: Depth (inches): Hydric Soil Present7 Yes No � Remarks , 1 `�� IIr�L �C� , 1 �5 s��:;, �b�i. ., b�i���� r�l,�o-3 .�,. ,� � �. q �.,, � 4. ,; , _ F fW �c�s� 'S Page 19 of 20 MICHAEL BAKER INTERNATlONAL US Army Corps of Engineers Eastem Mountains and Piedmont - Version 2.0 T�p; R-5735 Wetland: � WETLAND RATING WORKSHEET Fourth Version Project Name US 19/74/64/129 Nearest Road _,� ;�- :; f�� � 1 C County Cherokee Wetland area _ % acres Wetland width _�' �== ` feet Name of evaluator �J S�r r �; , 1 Date C� /� �- %/ � Wetland location _ on pond or lake �C on perennial stream � on intermittent stream _ within interstream divide other: Soil series: �.� i� _ predominantly organic - humus, muck, or peat � predominantly mineral - non-sandy _ predominantly sandy Hydraulic factors _ steep topography ditched or channelized � total wetland width > I00 feet Adjacent land use (within '/2 mile upstream, upslope, or radius) X forested/natural vegetation `� `` % �' agriculture, urban/suburban _f S % � impervious surface �% Dominant vegetation �1� � rr' ` Pr/ (2) �di /,�� h c- S /� a /_% �� : �^ �' � (3) �����., -��'t '��� � '"`Q����'�.-��3'�.S , Flooding and wetness _ semipermanently to permanently flooded or inundated �C seasonally flooded or inundated _ intermittently flooded or temporary surface water _ no evidence of flooding or surface water Wetland type (select one)� Bottomland hardwood forest Pine savanna � Headwater forest Freshwater marsh _ Swamp forest _ Bog/fen ' ' _ Wet flat � � _ Ephemeral �vetland � �+ a � � � � _ Pocosin _ Carolina bay Bog forest � Other: I�c��rJwu��� ;�•��ti� C�/LwA-ti �/ /4slo d�f -�r Jti r 1` /r.1� �-t/Fr�.r. Yy'1 a. 5� � The rating system cannot be applied to salt or brackish marshes or stream channels ----------------------- --------•• ---------------------•----•-------•------•----•--•------ ��R' Water storage � x 4.00 = � � A Bank/Shoreline stabilization � x 4.00 =� �'�'etland � rating � T Pollutant removal 1 " x 5.00 =� 1 Wildlife habitat J x 2.00 = � 3� N Aquatic life value ,�j x 4.00 = I� G Recreation/Education ( x 1.00 = 0 �** Add t point if in sensitive watershed and >IO% nonpoint source disturbance within'/, mile upstream, upslope, or radius Page20of20 I N T E R N AT I 0 N A L 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): R-5735 2. Date of evaluation: 8/21/18 3. ApplicanUowner name: NCDOT 4. Assessor name/organization: Dave McHenry 5. County: Cherokee 6. Nearest named water body 7. River basin: Hiwassee on USGS 7.5-minute quad: Hiwassee Lake 8. Site coordinates (decimal degrees, at lower end of assessment reach): 35.0739, -84.0469 STREAM INFORMATION: (depth and width can be approximations) 9. Site number (show on attached map): Site 2 and SC 10. Length of assessment reach evaluated (feet): 50 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 �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 mi2) ❑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/supplementarv measurements included in "Notes/Sketch" section or attached? I-IYes (-INo 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 Not A 3. Feature Pattern - assessment reach metric �A A majority of the assessment reach has altered pattern (examples: straightening, modification above or below culvert). ❑B Not A 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 Not A 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 � y ❑F 5% oysters or other natural hard bottoms (include liverworts, lichens, and algal mats) �@ ❑G Submerged aquatic vegetation ❑B Multiple sticks and/or leaf packs and/or emergent o�' ❑H Low-tide refugia (pools) vegetation � � ❑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) ❑ ❑ � ❑ ❑ Silt/clay (< 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% impenrious 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: Stream Site Name R-5735 Stream Category Mb1 Draft NC SAM Stream Rating Sheet Accompanies User Manual Version 2.1 Date of Assessment 8/21/18 Assessor Name/Organization Dave McHenry 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 Geo (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 NO NO Intermittent USACE/ All Streams LOW MEDIUM LOW LOW LOW LOW NA LOW LOW MEDIUM LOW NA NA NA NA NA LOW MEDIUM LOW LOW LOW YES MEDIUM NA LOW LOW MEDIUM MEDIUM LOW LOW LOW LOW LOW NA NA NA NA NA NA NA LOW NCDWR Intermittent LOW MEDIUM LOW LOW LOW LOW NA LOW LOW MEDIUM LOW NA NA NA NA NA LOW MEDIUM LOW LOW LOW YES NA NA LOW LOW MEDIUM MEDIUM LOW LOW LOW LOW LOW NA NA NA NA NA NA NA LOW 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): R-5735 2. Date of evaluation: 8/21/18 3. ApplicanUowner name: NCDOT 4. Assessor name/organization: Dave McHenry 5. County: Cherokee 6. Nearest named water body 7. River basin: Hiwassee on USGS 7.5-minute quad: Hiwassee Lake 8. Site coordinates (decimal degrees, at lower end of assessment reach): 35.0766, -84.0436 STREAM INFORMATION: (depth and width can be approximations) 9. Site number (show on attached map): Site 3 and SA 10. Length of assessment reach evaluated (feet): 50 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): 10 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 mi2) ❑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/supplementarv measurements included in "Notes/Sketch" section or attached? I-IYes (-INo 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 Not A 3. Feature Pattern - assessment reach metric ❑A A majority of the assessment reach has altered pattern (examples: straightening, modification above or below culvert). �B Not A 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 Not A 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 � y ❑F 5% oysters or other natural hard bottoms (include liverworts, lichens, and algal mats) �@ ❑G Submerged aquatic vegetation ❑B Multiple sticks and/or leaf packs and/or emergent o�' ❑H Low-tide refugia (pools) vegetation � � ❑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) ❑ ❑ � ❑ ❑ Silt/clay (< 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% impenrious 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: Stream Site Name R-5735 Stream Category Mb2 Draft NC SAM Stream Rating Sheet Accompanies User Manual Version 2.1 Date of Assessment 8/21/18 Assessor Name/Organization Dave McHenry 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 Geo (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 NO NO Perennial USACE/ NCDWR All Streams Intermittent LOW HIGH LOW LOW MEDIUM LOW NA MEDIUM LOW MEDIUM HIGH NA NA NA NA NA LOW HIGH LOW MEDIUM LOW YES MEDIUM NA LOW LOW HIGH MEDIUM LOW LOW LOW LOW LOW NA NA NA NA NA NA NA LOW 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): R-5735 2. Date of evaluation: 8/21/18 3. ApplicanUowner name: NCDOT 4. Assessor name/organization: Dave McHenry 5. County: Cherokee 6. Nearest named water body 7. River basin: Hiwassee on USGS 7.5-minute quad: Hiwassee Lake 8. Site coordinates (decimal degrees, at lower end of assessment reach): 35.078776, -84.040051 STREAM INFORMATION: (depth and width can be approximations) 9. Site number (show on attached map): Site 4 and SB 10. Length of assessment reach evaluated (feet): 25 11. Channel depth from bed (in riffle, if present) to top of bank (feet): 1 ❑Unable to assess channel depth. 12. Channel width at top of bank (feet): 2 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 mi2) ❑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/supplementarv measurements included in "Notes/Sketch" section or attached? I-IYes (-INo 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 Not A 3. Feature Pattern - assessment reach metric �A A majority of the assessment reach has altered pattern (examples: straightening, modification above or below culvert). ❑B Not A 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 Not A 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 � y ❑F 5% oysters or other natural hard bottoms (include liverworts, lichens, and algal mats) �@ ❑G Submerged aquatic vegetation ❑B Multiple sticks and/or leaf packs and/or emergent o�' ❑H Low-tide refugia (pools) vegetation � � ❑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) ❑ ❑ � ❑ ❑ Silt/clay (< 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% impenrious 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: Stream Site Name R-5735 Stream Category Mb1 Draft NC SAM Stream Rating Sheet Accompanies User Manual Version 2.1 Date of Assessment 8/21/18 Assessor Name/Organization Dave McHenry 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 Geo (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 NO NO Perennial USACE/ NCDWR All Streams Intermittent LOW MEDIUM LOW LOW MEDIUM LOW NA MEDIUM HIGH MEDIUM MEDIUM NA NA NA NA NA MEDIUM MEDIUM LOW LOW LOW NO MEDIUM NA LOW LOW MEDIUM MEDIUM HIGH LOW LOW LOW LOW NA NA NA NA NA NA NA LOW SC NC DWQ �tream Identi�cation Foritta Version 4.1I ��� �°°" �ate: �j .... �� Z d / � ProjectlSi#e: �_ 5���" Lati#ude: �� ��,� �valuator: � /�1f �� Cnuniy: �� �.. � Lor�gitude: � t�! t� � �� 4'" �. �^ iotal Po�nts: 5tream �etermina ircle onej Oth�r 5tream is at least infermiffent �J � �p�gme�a ntermiti nt erenl7ia[ e.g. Quad Name: if ? 99 or nerennial if ? 30" G' A. Geomor holo (Subtotal T C�.) '[� Continuity of channel bed ar�d bank 2. 5ir�uvsity of channel alang thalweg 3. In-chanr�el sfr�cture: ex. riffle-paol, step-poo[, ri le- ool se uence 4. Pa�ticle size of strearn substrate 5. Activelre[ict floodplain 6. Oepositionai bars nr benches 7. Recent alluvial deposifs 8. HeadcuEs 9. Grade control 1Q. Natura[ valley 11. 5econd or reater order channel art�ifieial ditches e not rafed; see discussiort in manual �� �. � ,._-..�-.,--,-- drolo (5ubtotal = A..S 12. Presence of Baseflow 13. fran oxidizing bacteria 14. Leaf {itt�r 15. S�diment on plan#s or debris 16. Orgartic debris lines or piles 17. Soil-based evidence of high water table? C. Biolo (Subtotal = �� 18. Fibrous raots in streambed Absen� 0 Weak _� � No�O� :�"� ��&�'1 a � 0 'I 1.5 0.5 4 0. No=O 3 Maderate 2 2 2 Yes=3 Yes 19. Roated uplar�d plants in streambed 3 2 � 2Q. Mac�ot�enthos (note dive€sity and ahundance) D 1 2 29. Aquatic Moilusks 1 2 22. Fish 0.5 1 23. Crayfish �.5 1 � 24. Amphibians 0 (3.5 1 25. A(gae 0 0.5 1 26. Wetland plar.ts in streambed FACW = �.75; OBL = 1.5 Olher "perenniai sfreams may also I�e id ntified using othar meihods. See p. 35 of manual. Notes: �At'k� 'G�r�,o �f�v'��+ �''� ��"s�..�.� �'�•,� � `% ov�`- r� � SlcetCh: � ��� f� _�� - n � � ��J �=• `� v� �� .�- � %�� �� .�--�`me.;.� ' h � � „ 3 3 3 3 3 3 3 3 1.5 '[ .5 0 1.5 1.5