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HomeMy WebLinkAbout20051290 Ver 1_Year 3 Monitoring Report_20120823os a RO McCain Stream Restoration Project Randolph County, North Carolina MY -03 Monitoring Report Data Collected: August 25, 2011 Submitted: December 2, 2011 r 'I*- LcoTtem ]dl l, reaaaiw Prepared for: North Carolina Department of Environment and Natural Resources Ecosystem Enhancement Program Parker Lincoln Building 2728 Capital Boulevard, Suite 1H -103 111 V� 11 OWN I naacigu, 114 %. /-iow RECEIVED AUG 2 3 2012 -WATER WAUIY Pit i i l; M oA STiOF 7ER MtA" DEC 0 2 2011 NC ECOSYSTEM ENHANCEMENT PROGRAM McCain Stream Restoration EEP Project #443 Sophia, North Carolina Randolph County MY -03 Monitoring Report Prepared By: Ward Consulting Engineers, P.C. Firm License Number C -2619 Project Manager: Becky Ward, P.E. 8368 Six Forks Road, Suite 104 Raleigh, NC 27615 -5083 Ph: 919 - 870 -0526 Fax: 919 - 870 -5359 McCain Stream Restoration Year 3 Monitoring Report NCEEP Project number: 443 Year 3 of 5 Ward Consulting Engineers, P.C. December 2011 i �i TABLE OF CONTENTS I Executive Summary 2 II Methodology 3 A Vegetation Methodologies 3 B Stream Methodologies 3 III References 4 APPENDICES r Appendix A Project Vicinity Map and Background Tables 5 �— Figure la Vicinity Map 6 Table la Project Components 7 Table lb Component Summations 7 Table 2 Project Activity and Reporting History 8 J Table 3 Project Contacts Table 9 Table 4 Project Attribute Table 10 Appendix B Visual Assessment Data 11 Figure 2 Consolidated Current Conditions Plan View 12 1 Table 5 Visual Stream Morphology Assessment Table 16 Table 6 Vegetation Condition Assessment Table 20 Photos 1-6 Stream Station Photos 22 Photos 7 -13 Vegetation Monitoring Plots Photos 25 Appendix C Vegetation Plot Data 29 Table 7 Vegetation Plot Criteria Attainment 30 { Table 8 CVS Vegetation Plot Metadata 31 I Table 9 CVS Planted and Total Stem Counts 32 Appendix D Stream Survey Data 33 Figure 3 Cross - Section 1 34 Figure 4 Cross - Section 2 35 1 Figure 5 Cross - Section 3 36 Figure 6 Cross - Section 4 37 Figure 7 Cross - Section 5 38 Figure 8 Cross - Section 6 39 Fi Figure 9 Longitudinal Profile 40 Figure 10 Pebble Count Plots - XS -1 41 r- Figure 11 Pebble Count Plots - XS -2 42 Figure 12 Pebble Count Plots - XS -3 43 - Figure 13 Pebble Count Plots - XS-4 44 Figure 14 Pebble Count Plots - XS -5 45 7 l f Figure 15 Pebble Count Plots - XS-6 46 - Table 10a Baseline Stream Data Summary 47 _ Table 10b Baseline Stream Data Summary 49 Table l la Dimensional Morphology Summary 50 +J Table l lb Stream Reach Data Summary 51 Appendix E Hydrologic Data 53 Table 12 Verification of Bankfull Events 54 Photo 14 Wrack Line 54 McCain Stream Restoration Year 3 Monitoring Report NCEEP Protect number 443 Year 3 of 5 Ward Consulting Engineers, P C December 2011 r I. ' Executive Summary The McCain Stream Restoration Site restored a total of 2;470 linear feet of stream in the Lower Yadkin River Basin The project site is situated in Randolph County in the Piedmont physiographic province of North Carolina and is in the Carolina Slate Belt ecoregion The project stream is an Unnamed Tributary to Back Creek (UTBC) From the confluence with UTBC, Back Creek flows approximately one mile to'Lake Lucas / Back Creek Reservoir The McCain Stream Restoration site is located on a 71 -acre parcel located approximately one mile southeast of the intersection of Lake Lucas Road (SR 1518) and Spero Road (SR1504) in Randolph County, North Carolina The property is an active livestock farm, and is surrounded by a mix of hardwood forests, row crops, and other livestock operations See Figure 1 Viciiuty'Map in Appendix A ' Project Goals • Restore a stable channel morphology that is capable of moving the flows and sediment provided by its watershed • Restore riparian buffer habitat and functions • Improve water quality to'the receiving watershed by reducing bank erosion and bed degradation 1 • Improve aquatic habitat Project Objectives • Build an appropnate'C4 channel with stable channel dimensions • Plant a functional Bottomland Hardwood'Forest community to create an effective riparian buffer ' • Exclude livestock from the riparian areas Seven vegetation monitoring plots (1 -7) were monitored for MY -03 Of these seven plots, plots 1, 2, 5, 6, and 7 are not meeting vegetation success criteria The vegetation success criteria have been met by 28% of the plots in momtonng,year MY 03 The success criterion for planted woody species,is 320 stems /acre after MY -03 A mortality rate of ten percent will be allowed after MY -04 (288,stems /acre), with another ten percent,allowed after MY -05 (260 stems /acre) Currently the site contains 289 planted stems /acre, excluding livestakes, which is'below the success criteria for MY -03 Total stem counts including natural -stems and livestakes resultedan 722 stems /acre Bare banks, areas of low stem densities, and invasive exotics are the only notable vegetation problem areas for MY -03 Invasive exotics within the conservation easement include tall fescue (Schedonurus arundinaceus), Japanese stiltgrass (Microstegium vimineum), multiflora rose (Rosa multiflora), Chinese lespedeza (Lespedeza cuneata), and Chinese privet (Ligustrum sinense) Although these species have been given different ranks of seventy, the functionality of the project is not expected to be impaired significantly It is likely that all of these species were present in and,adjacent to the conservation easement previous to construction The tall fescue and Japanese stiltgrass appears to be inhibiting. some growth of planted stems in . some areas, and there is very few successional woody stems were observed in the fescue dominated areas For additional information relating to vegetation, see Appendix C Approximately 4 acres have been identified for supplemental planting in the future but has not been scheduled by the time of this report McCain Stream Restoration Year 3 Monitoring Report NCEEP Project number 443 Year 3 of S Ward Consulting Engineers, P C December 2011 There has been little change in the stream pattern, profile or dimension between MY -02 and the present monitoring year MY -03 The stream lacked flowing water at the time of data collection, with a few isolated pockets of standing water In the majority of the stream length bedform features ar`e providing vertical stability throughout the project site_ In general, all pools are maintaining their depth with most of the very deep pools forming on the downstream side of structures The lack of flowing water made the assessment of properly functioning stream features difficult Throughout the'entire stream, the cross section dimensions have not significantly changed as compared to MY -02 Reach 1 is a short stream segment consisting of 286 linear feet in the upper most portion of the protect In this reach 100% of riffles and pools are stable and functioning as designed The riffle pebble count in this reach exhibits slight coarsening The visual assessment for Reach 1 reflected bank stability at 91% The total bank erosion length of 50 feet is a relatively small length of the total protect distance but resulted in a high percentage value due to the short reach length The bank erosion on the left bank at station 10 +25 was marked as an erosional feature however significant erosion has not occurred this year as compared to its condition in previous monitoring years The stream right bank, due to tie in constraints at the beginning of the project, is an extension of the steep valley slope The toe of the slope is stable however the bank supports woody vegetation at bankfull elevations perched on the slope with undercut roots The bank is not expected to fully stabilize due to lack of vegetation and the steep grade of the adjacent slope, however continued mass wasting is not anticipated Only two structures are located in Reach 1 The structure functionally rate was 50% for MY -03 due to signs of piping that were observed at the rock cross vane located at station 12+49 during the site visit conducted in March12011 Piping was not observed during the August 201.1 data collection due to a lack of flowing water The piping was occurring between the sill rock and vane arm and was viewed as, minor as it was not causing scouring or compromising the structure function The structure will be re- evaluated during the site visit in the spring of 2012 Reach 2 is 2250 linear feet and comprises the majority of the stream length In Reach 2, 94% of riffles and 89% of pools are functioning properly Thalweg centering appears to be an issue on approximately 24% of the upstream side of pools (Runs) and 6% of the downstream side of pools (Glides) This is primarily due to aggradathon, which appears in about 1% of the overall reach length The lack of centering is not causing bank erosion The structures in Reach 2 are showing afunctionahty of 100% throughout ,the reach and exhibit no signs of piping or integrity issues The banks of Reach 2 appear to be stable with no signs of new erosion ' Summary information/data related to the occurrence of items such as beaver encroachment and - statistics related to performance of various protect and monitoring elements can be found in the tables and figures in the report appendices Narrative background and supporting information formerly found in these reports can be found in the Baseline Monitoring Report (formerly Mitigation Plan) and in the Mitigation Plan (formerly Restoration Plan) documents available on EEP's website All raw data supporting the tables and figures in the appendices are available from EEP upon request McCain Stream Restoration Year 3 Monitoring Report NCEEP Project number 443 Year 3 of 5 Ward Consulting Engineers, P C December 2011 II. Methodology Methodologies follow EEP monitoring report template Version 1.3 (1/15/2010) and guidelines (Lee et al 2008). Photos were taken with a digital camera. A Trimble Geo XT handheld unit with sub -meter accuracy was used to collect vegetation monitoring plot origins, and problem area locations. Cross sectional and longitudinal surveys were conducted using total station survey equipment. Data was entered into AutoCAD Civil3D to obtain dimensions of the cross sections and parameters applicable to the longitudinal profile. Reports were then generated to display summaries of the stream survey. A. Vegetation Methodologies Level II of the EEP /CVS protocol Version 4.2 was used to collect data for the seven representative vegetation monitoring plots within the conservation easement for MY -03. Data collected for these plots are in Appendix C. B. Stream Methodologies Stream profile and cross - sections were surveyed using total station equipment and methods. The survey data was plotted using AutoCAD Civil3D. The longitudinal profile was generated using the MY -00 alignment. Cross sectional data was extracted based on a linear alignment between the end pins. Cross section bankfull elevations for yearly comparisons are based on the baseline bankfull elevation established for each cross section. III. References Lee, Michael T. Peet, Robert K. Roberts, Steven D., Wentworth, Thomas R. (2008). CVS -EEP Protocol for Recording Vegetation Version 4.2. Weakley, Alan (2007). Flora of the Carolinas, Virginia, Georgia, and Surrounding Areas. http:/ /www.herbarium.unc.edu /flora.htm. Wolman, M.G., 1954. A Method of Sampling Coarse River -Bed Material, Transactions of American Geophysical Union 35:951 -956. McCain Stream Restoration Year 3 Monitoring Report NCEEP Project number: 443 Year 3 of 5 Ward Consulting Engineers, P.C. December 2011 Appendix A. Project Vicinity Map and Background Tables I� L I McCain Stream Restoration I NCEEP Project number 443 Ward Consulting Engineers, P C i� Year 3 Monitoring Report Year 3 of 5 December 2011 CL N i d m 3i c f a 0 N W W Table 1 a. Project Components Table la. Project Components McCain Stream Restoration -Pro ect No. 443 Project Riparian Wetland Ac Restorat Upland Ac Footag BMP Non - Riverine Riverine 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 BMP 2417 Compone Existing Enhancement 1 Approac a or Stationin Mitigatio Mitigation Ele 0 nt or Feet/Acres ion h Acreag g n Ratio Units men Comment Reach ID 2417 Level 0 a 0 0 ts' Stream was 10+00— realigned and Reach I 490 If R P2 286 If 1 286 two cross 12 +86 vanes were installed Stream was realigned and six cross vanes were installed. A 53' length of Reach II 1955 If R P2 2184 If 12 +87 1 2131 channel 34 +70 through an easement exception has been excluded from the mitigation unit calculation. 1 = BR = Bioretention Cell; SF = Sand Filter; SW = Stormwater Wetland; WDP = Wet Detention Pond; DDP = Dry Detention Pond; FS = Filter Strip; S = Grassed Swale; LS = Level Spreader; NI = Natural Infiltration Area, O = Other, CF = Cattle Fencing; WS = Watering System; CH = Livestock Housing Table lb. Component Summations Table 1 b. Component Summations McCain Stream Restoration Site /Project No. 443 Restoration Level St ea m If Riparian Wetland Ac Non - Riparian Ac Upland Ac Buffer Ac BMP Non - Riverine Riverine 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Restoration 2417 Enhancement Enhancement 1 0 Enhancement II 0 Creation Preservation 0 HQ Preservation 0 Totals Feet/Acres 2417 0 0 0 0 0 MU Totals 2417 1 0 0 0 0 0 Non-Applicable McCain Stream Restoration Year 3 Monitoring Report NCEEP Project number: 443 Year 3 of 5 Ward Consulting Engineers, P.C. December 2011 Table 2 Project Activity and Reporting History Table 2. Project Activity and Reporting History McCain Stream Restoration Site /Project No. 443 Elapsed Time Since Grading Completer 2' yr 10 months Elapsed Time Since Planting Complete: _ 2 yr 10 Months Number of Reporting Years': 3 " Activity or Deliverable Data Collection Complete Completion or Deliver Restoration Plan 2003/2004 Jun -05 Final Design — Construction Plans f N/A May -06. - Construction N/A f Mar -09 Temporary seed mix applied to entire project area N/A Mar -09 Permanent seed mix applied to reach/segments 1 -4 N/A Mar -09 Mitigation Plan / As -built (Year 0 Monitoring — baseline) May -09 - ' Jul -09 Year 1 Monitoring Oct -09 Dec -09 Year 2 Monitoring Nov -10 Nov -10 Year 3 Monitoring Aug -11 Nov -11 Year 4 Monitoring Year 5 Monitoring 1 = Equals the number of reports or data points produced excluding the baseline McCain Stream Restoration NCEEP Project number 443 Ward Consulting Engineers, P C Year 3 Monitoring Report Year 3 of 5 December 2011 Table 3 Project Contacts Table Table 3 Project Contacts Table McCain Stream Restoration Site/Project No. 443 Designer KCI Associates of NC Landmark Center 11, Suite 220 4601 Six Forks Rd -' Raleigh, NC 27609 Primary project design POC Adam Spiller (919) 783 -9214 Construction Contractor Carolina Environmental Contracting, Inc PO Box 1905 Mount Airy, NC 27030 Construction contractor POC Stephen James (336) 320 -3849 Survey Contractor Survey contractor POC _ Planting Contractor Carolina Environmental Contracting, Inc PO Box 1905 Mount Airy, NC 27030 Planting contractor PO_ C Stephen James (336) 320 -3849 - Seeding Contractor Contractor point of contact Seed Mix Sources Company and Contact Phone Nursery Stock Suppliers Virginia Department of Forestry (504) 363 -5732 Monitoring Performers Ward Consulting Engineers, P C 8368 Six Forks Rd, Suite 104 Raleigh, NC 27615 Becky Ward (919) 870 -0526 Stream Monitoring POC Becky Ward (919) 870 -0526 Vegetation Monitoring POC Chris Sheats - The Catena Group - (919) 732 -1300 Wetland Monitoring POC Chris Sheats - The Catena Group - (919) 732 -1300 McCain Stream Restoration NCEEP Project number 443 Ward Consulting Engineers, P C Year 3 Momtormg Report Year 3 of 5 December 2011 Table 4 Protect Attribute Table Table 4 Project Attribute Table McCain Stream Restoration Site/Project No 443 Project County Randolph County Phystographic Region Piedmont Ecoregion Carolina Slate Belt Pro ect River Basin Yadkin USGS HUC for Project 14 digit) 3040103050050 NCDWQ Sub -basin for Project 03 -07 -09 Within extent of EEP Watershed Plan? No WRC Hab Class arm Cool Cold Warm % of proiect easement fenced or demarcated 100% Beaver activity observed during design phase? No Restoration Com onent Attribute Table Reach 1 Reach 2 Drainage area 0 88 sq mi 0 88 sq mi Stream order First First Restored length feet 286 2184 Perennial or Intermittent Perennial Perennial Watershed type Rural Urban Developing etc Rural Watershed LULC Distribution (e g) Urban Ag -Row Crop Ag- Livestock Forested Water/Wetlands 4% 16% 120/0 67% <1% Watershed impervious cover % 2° /G NCDWO AU /Index number 13 -2 -3 -3 UT Back Creek NCDWQ classification C 303d listed? No Upstream of a 3034 listed segment? No Reasons for 303d listina or stressor WA Total acreage of easement 12 9 Acres Total vegetated acreage within the easement 4 8 Acres Total planted acreage as part of the restoration 7 6 Acres Rosgen classification of pre-existing 134c C5 /E5 /C4 Rosgen classification of As -built 134c C4 I Valley type V V Valley sloe 00066 Valley side slope ranee g 2 -3 % 138%-326% Valley toe slope ranee q 2 -3 % 2 52% - 6 15% Cowardin classification N/A I N/A Trout waters desi nation No Species of concern endangered etc ? /N No Dominant soil series and characteristics Series Dogue Sandy Loam Dogue Sandy Loam Depth U U Clay-/. U U K I U U T I U U Use N/A for items that may not apply Use ---tor items that are unavailable and "U" for items that are unknown McCain Stream Restoration Year 3 Monitoring Report I NCEEP Protest number 443 Year 3 of 5 Ward Consulting Engineers, P C December 2011 I - i f� �I Appendix B. Visual Assessment Data �i i ((({ McCain Stream Restoration Year 3 Monitoring Report t� NCEEP Project number 443 Year 3 of 5 Ward Consulting Engineers, P C December 2011 it 4 P i ,;1,r _,�r� ` ' � � yj,�,,,• �,7 �- r 'S { , r _ � : � j� -'"'C 1,. lt'w LEGEND: U P"' PROBLEM AREA - CCC) Ln ; %� i r sal ✓�yJ �: vP -2 VEGETATION PLOT °N' Ln t9 m .w,; ,,i.. [. J 1,r' A :t". 3• - j N PHOTO POINT Ln VEGETA TION PROBLEM AREA o 0 BANK PROBLEM AREA - SCOURED /ERODING O co BANK PROBLEM AREA - UNDERCUT L m f BANK PROBLEM AREA - MASS WASTING yyd k°f3 l M1�r x PROBLEM AREA - MISCELLANEOUS per %'k STREAM PROBLEM AREA - DEGRADATION t CROSS SECTION M STREAM THALWEG ��Y`),M'fr' / �z" ' 1 CONSERVATION EASEMENT p STREAM CROSSING V S P STRUCTURE PROBLEM AREAS ` rta,d! Y` ✓. ���yf ` -, . -, -r. . 'r�r`'.'.' c'�..c. : /'`.F3"'!r`,l�.: =.a `�r'1�'+ t.�� ?,- oWik �. y -� M Vegatation Plot Pin Coordinate Table- (NAD83) Vegatation Pin 1 Pin 2 Pin 3 1 Pin 4 Northing Easting Northing Easting Northing Easting Northing I Easting Plot Number 1 734720.6 1746458.3 734703.2 1746430.5 734674.8 1746448.4 734691.7 11746476.8 1746732.4 2 734493.4 1746543.0 734476.2 1746571.3 734446.9 1746550.0 734465.4 1746523.3 3 734162.7 1746572.3 734168.9 1746541.4 734136.8 1746534.4 734130.7 1746567.2 4 733830.0 1746523.9 733863.9 1746517.8 733868.0 1746550.0 733835.2 1746556.2 5 733565.2 1746579.5 733597.1 1746572.7 733602.5 1746606.0 733570.7 1746613.3 _ 6 733365.1 1746622.0 733331.8 1746625.4 733336.5 1746657.3 733368.9 1746654.4 7 0 733124.5 1746641.1 733095.5 1746656.9 733080.5 1746628.0 733109.4 j 1746612.9 Cross Section Pin Coordinate Table (NAD83) ss Section Left Pin Right Pin Number Northing Easting Northing Easting 1746310.8 1746536.5 1 734735.9 734473.6 1746381.9 1745659.4 734750,7 734404.4 2 3 733888.1 1746462.6 733915.0 1746403.8 4 733744.3 746493.0 733773.5 1746430.1 5 733469.0 1746732.4 733442.5 1746673.0 6 733326.2 1746726.5 733291.0 1746668.6 GRAPHIC SCALE 150 0 75 150 300 W FEET ) 2010 Aerial from NCOne Map corn finch = 150 ft. 1 1 1 w I1, • •i 1 • • 1 M 13 APRIL 2011 27 OMDM 2011 MOM PROPEW �WME ocry MU 1, .150' sw a Ve atation Plot Pin Coordinate Table (NAD83) U-e I Pin 2 Pin 3 _�galafion Pin Pin 4 Ln Ln Plot Number Northing Easting Northing Easting Northing Easting Northing Easting '• 734720.6 1746458.3 734703.2 1746430.5 734674.8 1746448.4 734691.7 1746476.8 • 2 734493.4 1746543.0 734476.2 1746571.3 734446.9 1746550.0 734465.4 1746523.3 A-6 co VPA-7 3 734162.7 1746572.3 734168.9 1746541.4 734136.8 1746534.4 734130.7 1746567.2 W. a 8 P in 3 9 0 5 4 733830.0 1746523.9 733863.9 1746517.8 733868.0 1746550.0 733835.2 174 556.2 LL- 5 733565.2 1746579.5 733597.1 1746572.7 733602.5 1746606.0 733570.7 1746613.3 PP-7 crj 733368.9 1746 6 733365.1 1746622.0 733331.8 1746625.4 733336.5 11746657.3 654.4 7 733124.5 1746641.1 733095.5 1746656.9 73 3080.5 11746628.0 733109.4 1746612.9 VPA-5 Cross Section Pin Coordinate Table (NAD83) Wil Cross Section Left Pin Right Pin Number PA-6 19+00 PC Northing Easting Northing Eastin7g . ' 6 In Ra '.*V 7 1746310.8 1 734735.9 1746381.9 734750.7 2 734473.6 1745659.4 734404.4 1746536.5 3 733888.1 1746462.6 733915.0 1746403.8 PP. -6 4 733744.3 746493.0 733773.5 1746430.1 5 733469.0 1746732.4 733442.5 1746673.0 VP-2 6 1 733326.2 1746726.5 733291.0 1746668.6 j. v VPA-2 03 IL VPA-18 • d1k r VPA-1 PA-5 PA-2 p FF`FJ-4 PA-4 41, PP-3 LEGEND: p P"" E: A P MUOLLAVI Mn PP-1 7N VEGETATION PLOT PHOTO POINT DM 15 APW 201 PA-3 VEGETATION PROBLEM AREA I BANK PROBLEM AREA - SCOURED/ERODING 27 OGMW W11 • . 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'�..�i �. � ..,,,,, • �`• � • ..I113►J'1 rl q , �. - jlu[iiiie ,. 1 r L • !115111�j Ilil ••' '�„ _ r''7 - ' �Illii �,., :��, �'yr'.•" . � %R• `s'• 1 � .�1113nIA1. = ��' *•ter: •A - ' .' ' • Cross Section Pin Coordinate Table ;'iii j - ' � •','- , 1 '+ - W_ INT .Y .1 `�,�,. , •I• All PROBLEM AREA - `� .�•• (. ,t y _ � , .. • : • ' . � . • � L .. r • � • , • 1 • .._._. •,� :M't1 � t _tie.•.,: 'fit I;JCf111t,� h tt - a., 7 �, �' +. - �t .. • ._ MISCELLANEOUS . l' j s�•r. ♦ S C STREAM PROBLEM AREA - DEGRADATION GRAPHIC SCALE CROSS S ECTION STREAM THALWEG 50 0 25 so 100 CONSERVATION EASEMENT STREAM CROSSING ,,r� `.. 7 ` a • w PROBLEM AREAS 50 ft. I inch PROM NNE: hil l PROPERTY m Nile CCPV 200 OONE 1' . 50' aEfr w F0011L 2C Table 5 Visual Stream Morphology Stability Assessment Reach ID Reach 1 Assessed Length 286 Major Channel Category Channel Sub-Category Metric Number Stable, Performing as Intended Total Number In As -built Number of Unstable Segments Amount of Unstable Foota a %Stable, Performing as Intended Number with Stabilizing Woody Ve elation Footage with Stabilizing Woody Vegetation Adjusted % for Stabilizing Woody Ve elation 1. Bed 1. Vertical Stability ( Rrffle and Run units) 1. Aearadation - Bar formation/growth sufficient to significantly deflect flow laterally (not to include point bars) 100% 2. Dearadation - Evidence of downculting 1 30 90% 2. Riffle Condition 1. Texture /Substrate - Riffle maintains coarser substrate 2 2 100% 3. Meander Pool Cond"n 1. Depth Sufficient (Max Pool Depth : Mean Bankfull Depth 2:1.6) 3 3 100% 2. Length appropriate (>30% of centerline distance between tai( of upstream riffle and head of downstrem riffle) 3 3 100% 4.Thalweg Position 1. Thahveg centering at upstream of meander bend (Run) 3 3 100% r2, Thalweg centering at downstream of meander (Glide) 2 2 100% 2. Bank 1. Scoured/Eroding Bank lacking vegetative cover resulting simply from poor growth and/or scour and erosion o 100% 100% Banks undercut/overhanging to the extent that mass wasting appears 2. Undercut likely. Does hM include undercuts that are modest, appear sustainable and are providing habitat. 1 50 91% 91% 3. Mass Wasting Bank slumping, calving, or collapse 100% 100% Totals 1 50 91% 0 0 91 3. Engineered Structures 1 Overall Integrity Structures physically intact with no dislodged boulders or logs. 2 2 0 100 /° 2. Grade Control Grade control structures exhibiting maintenance of grade across the sill. 2 2 100% 2a. Piping Structures lacking any substantial flow underneath sills or arms. 2 2 100% 3. Bank Protection Bank erosion within the strictures extent of influence does = exceed 15 %. (See guidance for this table in EEP monitoring guidance document) 2 2 100% 4. Habitat Pool forming structures maintaining - Max Pool Depth : Mean Bankfull Depth ratio 21.6 Rootwads/logs providing some cover at base -flow. 2 2 100 Table 5 Visual Stream Morphology Stability Assessment Reach ID Reach 2 Assessed Length 2184 Adjusted % Number Number with Footage with for Major Stable, Total Number of Amount of %Stable, Stabilizing Stabilizing Stabilizing Channel Channel Performing Number in Unstable Unstable Performing Woody Woody Woody Category Sub-Cateaory Metric as Intended As -built Se ments Footage as Intended Vegetation Vegetation Vegetation 1. Bed 1. Vertical Stability (Riffle and Run units) 1. Aaaradation - Bar formation/growth sufficient to sgnificandy deflect flow laterally (not to include point bars) j 30 99 2. Degradation - Evidence of downcutting 1 125 94% 2. Riffle Condition 1. Texture /Substrate - Riffle maintains coarser substrate 16 17 94% 3. Meander Pool Condition 1. Depth Sufficient (Max Pool Depth: Mean Bankfull Depth > 1.6) 16 18 89% 2. Length appropriate (,30% of centerline distance between tail of upstream riffle and head of downstrem riffle) 18 18 100% 4.Thalweg Position 1. Thalweg centering at upstream of meander bend (Run) 13 17 76% 2. Thalweg centering at downstream of meander (Glide) 16 17 94% 2. Bank 1. Scoured/Eroding Bank lacking vegetative cover resulting simply from poor growth and /or scour and erosion 100 % 100 Banks undercut/overhanging to the extent that mass wasting appears 2. Undercut likely. Does N�T include undercuts that are modest, appear sustainable 100% 100% and are providing habitat. 3. Mass Wasting Bank slumping, calving, or collapse 100% 100% Totals 0 0 100% 0 0 1001/1, 3. Engineered Structures 1 Overall Integrity Structures physically intact with no dislodged boulders or logs. 8 8 100 2. Grade Control Grade control structures exhibiting maintenance of grade across the sill. 8 8 100% 2a. Piping Structures lacking any substantial flow underneath sills or arms. 8 8 100% 3. Bank Protection Bank erosion within the structures extent of influence does not exceed 15 %. (See guidance for this table in EEP monitoring guidance document) 5 6 83 4. Habitat Pool forming structures maintaining - Max Pool Depth : Mean Bankfull Depth ratio > 1.6 Rootwads/logs providing some cover at base -flow. 6 6 100 Criteria. Definitions and Thresholds for Visual Stream Morpholoav Assessments Major Channel Chanel Sub. Cat, o G7 o Metrk DMinklans Cafthmina Threshold OcPv 1, Bed 1. •rdoW 91.tl1 sue mo•to PoHk sro Run .old) gArtlik. a filling of pock a o bolos b•.dbrr akYanm.. An yeadng laser ffi dffin chrcMatl by send m•loft(uN El l) Mo k r Iwd 15 rr11n kngn a2p%.1 Raw! Ime lomntlm /poMh wlm emockeW fNlp d meet substrrie Md rnmlhng W M ntlt Imp pafu. to dM&Nun Ingih, ~o,00 k lose. NepRadM sew eiRiNkarlt nocph m tleflmd lbw aBarsl latkm ahaAd W utroPm. Red rlt aopdda n a k•Y ad F .wwdra RpNd appredetlm. (Soo Wtdo MddNt t bWOw fa mP A rsnpk hr ple emyaggntleun) 2. Numbr ntl a2. A adders tlontcuffi wXMn PorllaRun unit. • pml•a• hMraPYAyapc.d mrynewoo gr.tls control, tlprooabNtlorrnadtlnp k mq•dM my F soar, sbp my H lams has moot d pie dircerknn dwaibed Inplo. 'Indcamr• bWd• pndnd WI donna bM ttdps' ni deMrbh pent mabXW. ma loft (roll E12) are k a 15 feat in Inge a 2c% d aspdb.dnfm•trimeb•rkln .W —y, or ocarwdMewb.trsFt mlmmph mryWngrprde savoys adXlakun Inptn, wntheeklose. is tlwvn w etalrys Noub wppat n M•Ymnl d ntl perhaps dew wM run py. should Imp'Ra1M end sa. eeRadaNm wn.l. M dwr.w.mnt.a whey o.rlw. J. A . 10111. Cmdtlon 1.7pyQ Mould maF4F a mranses elmb m lh chain dabWtlm. d er rM. wean A IA rim welar ni la M rNM. Repo p. bbl. auto WaM rippar an ems•pnrn drab lining whr. amn Isua sorb; gaRr. 2 oaaw lesaaa�:a M„Ixldba Ia amdcama arvMn :). no� pools oral dw dWm t•R.d naafis M pole wil b ooekd.d re tWW here rM undr th• HAMA 9NCadpry aay. m• max bMkbd dgth Marti d 1.6 Woe M moon b.Mful dapih (Max Pod Doom : Moon B.ddul Dope, > 1.6). mac bnMul daps hon M A•- Wbksaku wrvry an be ulitatl m eau ask datrmnatlm. Ed .N, omw rwklum pool d.pib• using m• 1.6 multlplr fa • mq• d own &—.1 Wrie depn• ma typfy r -aadon Ral.cffi. 2. Lft=aWOped? Too moob wr only be applied In ..Ww pook, Ito mwrer pool knpm MaM be a of th • -iwn N NA norin• dance b•dwan to tW of the upon— dirk and to .121. daenomeen rel•. Tlulwg p w 1. Thaooeg —lo,lng ri upelneonof moon to Mad p t eb. NA A a M.. bnkn nor bra apoA bW V tin oriented larrbm•wlr b•A too in WOn Mond px Ratrrtdllmkaoomq•cffidm ry Folcs Mpai0 ng(MOdbrkarulm. SMrly,Mp ce to ,,kW inn re• ROe pahantarbblMook A2 brMrl. ThacunrtPyrr drWuep ooaMadnMCCPV IIya•en a n ink eaaaemrrt . ThAeog —Ming d tloanatrarn d a-- bare (GHe)'! Moot e.t abort NA NA 2 Bank 1. Soaur•dmrodnp Bank earla an euldMa srrHa IMOaan straw. Nelgl Lnglh Psl -.,al .nr.'a t0:1 Iwlow Tlso In om•r to borer, ease conlrum bank roobn uk, IWW brie W— s an dtermclrlsd rlh napW V the pradatY sea ktt ...mart d.,.WLdng ngomOon. faWnuM roobn ri k for a ghn be* nm "y rrdlay at>YdiM doArw.rea by .gaunt mriu• Ympmarin rxla •Lbrdnp nor.. One a lea• msNn in cbe• Raknky (ap. 10 rr o lose) a dWwe nt.grrlm d roe roes. rNlin dwbre leis sew A 6 3-6 8 A 10 . Wd— at orar n p to • •td w the ease woo . eppoora Y. untlMMe ri ..pprr waunatlstffitle nor r• provldlnp tetlta. nP' TMs table Raked a Wilda kr wmla,g mruhalds for d ram P—W m• WyFO of a Ow bark djwt inb M •dfmW "A Mmgxy rd" b rbk d YWRY(Ggkmm lL 9(1hk JaW AM MW. E.—"Y• MU P%" d.m.s dnxiq tlnWY and my. ft— SENla.rwmrn)sewed1.be- *ftMhwm. be* era" calaognymepphlg beuo m bank hoOt. Fmrwbeneepp! WIWIStl. gerund For d-CA- balk b be rneppee eld 181bd lo apo;tlkd. For Burgle, _ . WooWoodrtp where basks ere A feW high. sly map an uretahle sepnmt X N is Z 10 laa.' Stru es I. Ownll hd•prhy wont d npiurM ebudure pXamnn etwM Fete• al struduse roar proWds gnW control. bark d abutlue WYacWY Inffid wXh ro oleladpstl pouldre a bP' l)dnp talons a solo• odoo moon to maFffiIn lagbity, "as Rabdim, a hooXa hncpaw. Tleoo M cIe Vres, J -hods. nd a—elo, da. trucWrs a ih n 1 H arucWra iabn h® ococnM 2 Tmd, C —m acmtr avast •nKWr• No widW Ion d bod d.adKn m d yupeewn 0 Ming Man. or momma rmoorw to me nl.nk y, nndm. trtKmnT Son. plping b—F na catWMb. b•a d grade —.d. tructrtr•wtlh red'G' X amdua hs b.t gratl. mnhol 2a. Rog m arucWrea nY n moo • a nand roc.. lldrtp o or mwoo m m roods truoarr.wlln rmd- N apdfkam piping hee aaunad . BaAc Raec6on a sin—a ti manta d b �a/rWw aey a.om0 rrwmm y, nn.td• aFibnu rasmb15 %a Mtaelling erWdin rmd'B'N emceesnw r.W mRodin bask ofk�m• —,dn, Me o-tekrw.pnmrm a nitMtar. inn M ebYCpa• eMtM N d..Nkd wgptl•addnp.darr•b.Wt praeAm n dm"berk sea offidim • era ter. P— . wtlm a 1. moor- v aalM awn tom nnatek booabw rd Roaolrb our. a0 .0- 0 on-aam k nal Ro.Ybq helft Exhibit 1. Examples of bar features warranting concerning related to cataloging item 1.1.1 of the assessment Exhibit 3. Residual Pool Depth Table - Relating 1.6 criterion for typical mean riffle depths to residual pool depths This residual pool table was provided in the event the tracking of bankfull at each pool feature to estimate a Dmax was inconvenient. Estim[ the residual pool depth by measuring the max pool depth to water surface and subtracting the water depth at the riffle head may provide a n convenient way under certain circumstances to estimate in the field. For this reason the exhibit table provides a relationship between the criterion applied to mean riffle depth for the site and the resulting residual pod depths. Mean Riffle Depth D„a Multiplier Iler Target Pool Pool M Max Residual Pod Depth ---.- Water surface Rifne Crest Depth • i' Red" _..\ si , _ _! Riffle Goat From: Hilton and flab, 1993 1.0 1.6 1.6 0.6 145 1.6 2.4 0.9 2.0 1.6 3.2 1.2 2.5 1.6 4.0 1.5 3.0 1.6 4.8 1.8 3.6 i.6 5.6 2.1 1 4.0 1.6 6.4 2.4 4.5 1.6 7.2 2.7 5.0 1.6 8.0 3.0 1 5 = The above was developed because of the need to have a threshold given the large number of performers and to avoid spending time trying to catalog and map small objects that if excluded would have minimal overall impacts on the performance percentages. N is a guide that tries to strike a balance between the obvious need to have a threshold, yet provide confidence that the site conditions are accurately represented. For example, a scenario where 1 objet( nearly exceeding the threshold were to occur every 100 feet of bank height (which would be a high frequency and unlikely) with a bank height of 5 feet, would yield an error of -3 %. However, t the observer is encountering a truly high number of objects lust below the threshold in the above table (e.g. > 1 per 100 feet of bank :hannel on average) and is concerned that the exclsuion of such objects is going to misrepresent the she conditions, then judgement should be applied and objects below the threshold may be cataloged. If a rare -ondtion as described does occur and the thresholds are not utilized then a table footnote explaining this should be included. _astly, given the increase in overall area and the implications to stability, greater banks heights required smaller threshold minimums. Exhibit 2. Grephic dspicOV embedding of riffles with tine material pm*ng from top to bottom, the series of graphics to the cis the fining of intershal spaces between coarser panicles. T xibes increasing levels of embededness in riffles. The obser 1 have an understanding of the intended sutxtr ibutionsnlexture of the bed for the projects riffles when assess However, as a guideline for streams in the coarse gravel tie range, the 2nd panel from the top represents a via eline for the condition that would begin to elicit concern for t meter, but still contains a good deal of coarse meter teasing from that state to the conditions depicted in the the 4th panel represents a visual qua for significant emdedding. Exhibit 4. aOant of BtruotwM Influence for Bank Protection The drawing Is a guideline for the extent d Influence van arm.. I n stream bank.. The bracketed egl segment 11of) ImmWl.oaly, adjacent m the wife 5loot 6 feat am Is multiplied by 5 to datennine "total length of bank Influenced by a cross van. This includes phis bank length still acant to each vet emt, 1 length (10 kid) below each van arm. and % length 15 feet) on each bank above me uppermost structural element (In this tees the vane ale), yielding 50 feet 10 feat _10 feat in this example case. In this example a single arm vane orj -hook would only Influence 25s of bank. N the amount d nacent bank erosion d wca than within the extent inan exceeds 16 %Men ate structure le deemed rim to be Providing adagwb bank Protection In the above examples tlda would amour! b - 8 and 4 feet. raspactively. 10 bid 10 feet N In an erl er assessment the structure felled the 15% bank protection shade but the eroalon he. subsequently stabilised, than the observer can use beat proleselon.l judgment to determine N the structure is currently meeting the bank protection criteria. McCain Property Table 6 Veaetation Condition Assessment Planted Acreage 7.98 Easement Acreage 13.34 e etation Cateno Definitions Mapping Threshold CCPV De iction Number of Polvoons Combined Acreage % of 4. Invasive Areas of Concern Microstegium, tall fescue, multiflora rose, Chinese privet, Chinese lespedeza Mapping CCPV Number of Combined Planted Ve etation Cateoory Definitions Threshold De iction Polygons Acreage Acreage 1. Bare Areas Very limited cover of planted woody and herbaceous material on stream banks 0.1 acres Solid Yellow 3 0.01 0.1 Woody stem densities clearly below target levels based on visual observations and MY3 stem 2. Low Stem Density Areas 1count 0.1 acres Solid Orange 6 3.32 41.6 criteria. Total 9 3.33 41.7 3. Areas of Poor Growth Rates or Vigor Areas with woody stems of a size class that are obviously small given the monitoring year. 0.25 acres N/A 0 0.00 0.0% Cumulative Total 9 1 3.33 1 41.7% Easement Acreage 13.34 e etation Cateno Definitions Mapping Threshold CCPV De iction Number of Polvoons Combined Acreage %of Easement Acreage 4. Invasive Areas of Concern Microstegium, tall fescue, multiflora rose, Chinese privet, Chinese lespedeza 1000 SF Hatched 15 3.96 29.7 Easement Encroachment Areas Microstegium encroachment none Hatched 7 2.58 19.3 = Enter the planted acreage within the easement. This number is calculated as the easement acreage minus any existing mature tree stands that were not subject to supplemental planting of the understory, the channel acreage, crossings or any other elements not directly planted as part of the project effort. = The acreage within the easement boundaries. = Encroachment may occur within or outside of planted areas and will therefore be calculated against the overall easement acreage. In the event a polygon Is cataloged into items 1, 2 or 3 in the table and is the result of encroachment, the associated acreage should be tallied in the relevant item (i.e., item 1,2 or 3) as well as a parallel tally in item 5. = Invasives may occur in or out of planted areas, but still within the easement and will therefore be calculated against the overall easement acreage. Invasives of concern /interest are listed below. The list of high concern spcies are those with the potential to directly outcompete native, young, woody stems in the short-term (e.g. monitoring period or shortly thereafter) or affect the community structure for existing, more established tree /shrub stands over timeframes that are slightly longer (e.g. 1 -2 decades). The low /moderate concern group are those species that generally do not have this capacity over the timeframes discussed and therefore are not expected to be mapped with regularity, but can be mapped, it in the judgement of the observer their coverage, density or distribution is suppressing the viability, density, or growth of planted woody stems. Decisions as to whether remediation will be needed are based on the integration of risk factors by EEP such as species present, their coverage. distribution relative to native biomass, and the practicality of treatment. For example, even modest amounts of Kudzu or Japanese Knotweed early in the projects history will warrant control. but potentially large coverages of Microstegium in the herb layer will not likley trigger control because of the limited capacities to impact tree /shrub layers within the timeframes discussed and the potential impacts of treating extensive amounts of ground cover. Those species with the "watch list" designator in gray shade are of interest as well. but have yet to be observed across the state with any frequency. Those in red i ics are of particular interest given their extreme risk.!threat level for mapping as points where isolated specimens are found, particularly ealry in a projects monitoring history. However. areas of discreet. dense patches will of course be mapped as polygons. The symbology scheme below was one that was found to be helpful for symbolzing invasives polygons, particulalry for situations where the condition for an area is somewhere between isolated specimens and dense, discreet patches. In any case, the point or polygorVarea feature can be symbolized to describe things like high or low concern and species can be listed as a map inset. in legend items if the number of species are limited or in the narrative section of the executive summary. High Concern: Low/Moderate Concern: Vines Genus/Species Shrubs/Herbs Genus/Species Shrubs/Herbs Genus/Species Kudzu Pueraria lobata Japanese Knotweed Pol onum cus idatum Japanese Privet Li ustrum Ja onicum Porcelain Berry Am elo sis brevi eduncu Oriental Bittersweet Celastrus orbiculatus Gloss Privet Li ustrum lucidum Japanese Hone sucklc; Lonicera japonica Multiflora Rose Rosa multiflora Fescue Festuca spp. Japanese Hops Humulus japonicus Russian olive Elaea nus an ustifolia English Ivy Hedera helix Wisterias Wisteria spp. Chinese Privet Li ustrum sinense Microste ium Microste ium vimineum Winter Creeper Euon mus fortunei Chinese Silver grass Miscanthus sinensis Burning Bush Euon mus alatus Bush Killer Watch List Ca ratia'a onica Phra mites Phra mites australis Johnson Grass Sor hum hale ense Bamboos Ph llostach s spp Bush Honeysuckles Lonicera, s rees Sericea Les edeza Sericea Les edeza Periwinkles Vinca minor ee of Heaven Ailanthus altissima Garlic Mustard Watch List Alliaria etiolata Morning Glories Morning Glories Mimosa Albizia julibrissin Co on Grass Watch List Im erata c lindrica Bicolor Les edeza Watch List Les edeza bicolor Princess Tree Paulownia tomentosa Giant Reed Watch List Arundo donax Chinese Yams Watch List Dioscorea oppositifolia China Berry Melia azedarach Tro ical Soda Apple Watch List Solanum viarum Air Potato Watch List Dioscorea bulbifera Gallery Pear P rus calle ana Ja anese S irea Watch List S iraea japonica a anese Climbing Fern Watch List L odium a onicum hite Mulberry Morus alba Ja anese Barber Watch List Berberis thunber ii Tree Watch List Triadica sebifera Stream Station Photos Photo 1. Looking downstream at XS -1 Photo 2. Looking downstream at XS -2 McCain Stream Restoration Year 3 Monitoring Report NCEEP Project number: 443 Year 3 of 5 Ward Consulting Engineers, P.C. December 2011 ` �'� �'� �, . yE„ T i• r,�Y�' .ANY t Photo 3. Looking downstream at XS -3 'S Photo 4. Looking downstream at XS -4 McCain Stream Restoration Year 3 Monitoring Report NCEEP Project number: 443 Year 3 of 5 Ward Consulting Engineers, P.C. December 2011 XS_3 t q -- r,K S Photo 3. Looking downstream at XS -3 'S Photo 4. Looking downstream at XS -4 McCain Stream Restoration Year 3 Monitoring Report NCEEP Project number: 443 Year 3 of 5 Ward Consulting Engineers, P.C. December 2011 Photo 5. Looking downstream at XS -5 Photo 6. Looking downstream at XS -6 McCain Stream Restoration Year 3 Monitoring Report NCEEP Project number: 443 Year 3 of 5 Ward Consulting Engineers, P.C. December 2011 Vegetation Monitoring Plots Photos 9 P��1tt•.F%�ni� +�.�:9� .ai►�:�" 'rte Photo 7. Vegetation Plot 1 (September 8, 2011) Photo 8. Vegetation Plot 2 (September 8, 2011) McCain Stream Restoration Year 3 Monitoring Report NCEEP Project number: 443 Year 3 of 5 Ward Consulting Engineers, P.C. December 2011 Photo 9. Vegetation Plot 3 (September 8, 2011) Photo 10. Vegetation Plot 4 (September 8, 2011) McCain Stream Restoration Year 3 Monitoring Report NCEEP Project number: 443 Year 3 of 5 Ward Consulting Engineers, P.C. December 2011 Y y Photo 11. Vegetation Plot 5 (September 8, 2011) Photo 12. Vegetation Plot 6 (September 8, 2011) i, McCain Stream Restoration Year 3 Monitoring Report NCEEP Project number. 443 Year 3 of 5 Ward Consulting Engineers, P.C. December 2011 { i r ' �. r �. a +, ... ' �y �Fy1 .�, f4-e '•�, y�.n_�, .. :t :�:. Photo 13. Vegetation Plot 7 (September 8, 2011) McCain Stream Restoration Year 3 Monitoring Report NCEEP Project number: 443 Year 3 of 5 Ward Consulting Engineers, P.C. December 2011 ri � ~I -J : 117 LI McCain Stream Restoration 4f NCEEP Project number 443 Ward Consulting Engineers, P C Appendix C. Vegetation Plot Data Year 3 Monitoring Report Year 3 of S December 2011 Table 7 Vegetation Plot Criteria Attainment Vegetation Plot ID Vegetation Survival Threshold Met? Tract Mean VP 1 No VP 2 No VP 3 Yes VP 4 Yes 100% VP 5 No VP 6 No VP 7 No McCain Stream Restoration Year 3 Monitonng Report NCEEP Project number 443 Year 3 of 5 Ward Consulting Engineers, P C December 2011 - Table 8 CVS Vegetation, Plot Metadata - - - - McCain Stream Restoration Site/Project No 443 ' - - Report Prepared By - The Catena Group database name McCain property mdb r DESCRIPTION OF WORKSHEETS IN THIS DOCUMENT -- - - - - Description of database file, the report - - worksheets, and a summary of project(s) Metadata and project data Each project is listed with its PLANTED stems per acre, for each year This Prof, planted excludes live stakes Each project is listed with its TOTAL stems per acre, for each year This includes live stakes, all planted stems, and all Prof, total stems natural/volunteer stems List of plots surveyed with location and summary data (live stems, dead stems, Plots missing, etc Frequency distribution of vigor classes for Vigor stems for all plots Frequency distribution of vigor classes Vigor by Spp listed by species List of most frequent damage classes with number of occurrences and percent of total Damage stems impacted by each Damage values tallied by type for each Damage by Spp species Damage by Plot Damage values tallied by type for each plot A matrix of the count of PLANTED living stems of each species for each plot, dead Planted Stems by Plot and Spp and missing stems are excluded PROJECT SUMMARY - - __�_�____�__ Project Code 443 project Name McCain Stream restoration site located in the Description Yadkin River Basin River Basin length(ft) 2450 stream -to -edge width (ft) 50 area (sq m) 2275894 Required Plots (calculated) 7 Sampled Plots 7 McCain Stream Restoration Year 3 Monitoring Report NCEEP Project number 443 Year 3 of 5 Ward Consulting Engineers, P C December 2011 EEP Project Code 443. Project Name: McCain Table 9: Planted and Total Stem Counts Current Plot Data (MY3 2011) 1 Annual Means Scientific Name Common Name Species Type E443 -A -0003 1 E443- A-0002 E443 -A -0003 E443 -A -0004 I E443 -A -0005 E443 -A -0006 E443 -A -0007 MY312011) MY2(2010) PnoLS P -all T PnoLS P -all T PnoLS P -all T PnoLS P -all IT JPnoLS P -all T PnoLS P -all T PnoLS P -all IT PnoLS P -all IT PnoLS P -all T Acerne undo boxelder Tree 1 4 5 Betula nigra river birch Tree 2 2 2 1 1 1 6 6 6 3 3 3 1 1 1 4 4 4 11 1 1 18 18 18 18 18 18 omus amomum silky dogwood Shrub 8 8 1 1 1 3 3 1 1 1 1 5 5 3 18 18 3 18 18 Dias yros vir iniana common persimmon Tree 1 1 1 2 5 Fraxinus pennsylvanica green ash Tree 2 2 41 1 1 2 1 1 4 2 1 14 4 4 27 4 4 4 Liquidambar styraciflua sweetgum Tree I I 1 1 4 5 9 Liriodendron tulipitera tulipiree Tree 3 3 3 11 1 1 1 11 2 5 5 6 5 51 5 Platanus occidentalis American sycamore Tree 1 1 1 5 5 5 1 1 1 1 11 1 1 1 1 1 91 9 9 9 9 9 uercus falcata southern red oak Tree 2 2 2 2 2 2 3 3 3 uercus pagoda cherrybark oak Tree 2 2 2 2 2 2 1 1 1 uercus hellos willow oak Tree 5 5 5 1 1 1 1 1 1 7 7 7 6 6 6 Rosa multdora multiflora rose Shrub Vine 1 1 alix n ra black willow Tree 7 7 1 8 8 7 7 alix sericea silky willow Shrub Tree 1 1 4 4 3 3 8 8 8 8 Stem count size (ares) size (ACRES) Species count Stems per ACRE 7 7 7 4 20 23 18 18 20 8 8 12 3 11 20 6 6 7 4 1 11 36 50 811 125 49 79 79 1 1 1 1 1 1 1 7 7 0.02 0.02 0.02 0.02 0.02 0.02 0.02 0.17 0.17 2 2 2 3 6 7 6 6 7 5 5 6 3 6 10 3 3 4 4 5 9 8 10 1 8 10 10 283.3 283.3 283.3 161.9 809.4 930.81728.41 728.41 809.4 323.71 485.6 121.41 445.2 809.4 242.81242.81283.3, 161.91445,21 14571 289.11468.31 722.7 283.31 456.71 456.7 I_, Appendix D. Stream Survey Data I 0 McCain Stream Restoration Year 3 Monitoring Report _ NCEEP Project number 443 Year 3 of 5 Ward Consulting Engineers, P C December 2011 I� I I Project: MoCaln Property Summa bankfull Crass Section: Cross Section 1 MYO MYt MY2 MY3 MY4 MY5 Feature Riffle Reach 1 A (BKF) 18.6 20.8 18.7 17.8 Station: 12 +11.30 W (BKF) 16.9 17.2 18.1 16.2 Date: 8/25/11 Max d 1.5 1.6 1.6 1.7 Crew: BW, ZAP, SY Mean d 1.1 1.2 1.0 1.1 WID 15.4 14.2 17.5 14.6 MYOO.2009 MYOt -2009 MY02.2010 MY03 -2011 Station Elevation Notes Station Elevation Notes Station Elevation Notes Station Elevation Notes 548.39 LPIN 548.39 LPIN 548.39 LPIN 548.39 LPIN 6.50 547.76 0.30 548.19 0.10 548.26 0.05 548.29 14.00 546.79 6.00 547.72 2.80 548.15 5.83 547.82 ...�. . 21.10 546.16 13.40 546.76 9.25 547.37 12.62 546.94 ~ ... 25.50 545.21 22.10 545.85 14.42 546.82 20.31 546.45 30.60 544.82 34.10 543.31 TOBLBKR 24.30 27.40 545.16 545.05 21.29 24.14 546.18 545.36 24.04 28.52 545.38 545.04 xs 36.20 543.19 29.40 544.79 26.88 545.13 30.27 545.03 TOBL BKFIL i ! 38.70 543.11 30.60 544.68 TOBL BKFL 30.72 544.75 TOBL EIKH 32.31 544.35 40.50 543.01 42.80 543.01 32.30 33.90 544.06 543.25 32.01 34.33 544.09 543.58 34.81 36.83 543.63 542.97 TOE L ° 45.20 542.91 TW 35.60 542.88 35.79 543.04 TOE L 38.90 542.70 TW (! 45.70 543.12 37.40 542.76 37.32 542.96 41.08 542.85 47.10 543.83 38.30 542.66 TW 38.96 542.80 TW 43.22 $43.04 48.40 544.42 rOBR BKFF 40.60 542.70 40.26 542.86 45.19 542.99 TOE R 54.20 545.10 42.60 542.84 4210 543.01 46.40 543.72 'fly 56.50 545.81 45.50 542.84 44.62 543.00 TOE 47.56 543.93 59.70 546.45 46.60 543.50 45.27 543.34 48.93 544.72 rOBR 64.50 547.03 48.70 544.32 rOBR BKFF 47.77 543.97 52.94 544.89 69.00 547.76 52.70 544.82 50.16 544.56 rOBR BKF 54.97 545.21 72.60 548.15 RPIN 55.60 545.44 53.54 544.93 57.36 546.08 58.50 546.15 57.71 545.95 61.77 546.79 62.40 546.77 61.30 546.66 66.47 547.42 67.40 547.45 65.01 547.13 72.63 548.02 Photo of XS -1, looking in the downstream direction 71.90 547.93 68.96 547.59 72.79 548.25 RPIN 72.70 548.13 RPIN 72.76 547.99 72.79 548.14 RPIN Cross Section 1 549.00 548.00 547.00 546.00 c 0 Qa 545.00 W 544.00 543.00 54200 0.00 10.00 20.00 30.00 40.00 50.00 60.00 70.00 80.00 Station (Feet) +- As -Built --a Year 1 -*- Year 2 -a- Year 3 BKF Project: McCain Property Summa banklull LM MY1 MY2 MY3 MY4 MY5 Cross Section: Cross Section 2 Feature Riffle Reach 2 A (BKF) 33.7 42.7 44.4 43.3 Station: 16 +25.07 W (BKF) 24.6 25.2 28.0 26.3 Date: 8/25111 Max d 1.8 2.5 2.6 2.6 Crew: BW, ZAP, SV Mean d 1.4 1.7 1.6 1.6 W/D 18.0 14.9 17.6 16.0 •`� A� '� MY00 -2008 MY01 -2009 MY02.2010 MY03.2011 Station Elevation Notes Station Elevation Notes Station Elevation Notes Station Elevation Notes 'r r 543.01 LPIN 543.02 LPIN 543.01 LPIN 543.03 LPIN 8.50 542.71 1.30 542.72 0.10 542.79 0.09 542.81 16.90 542.73 11.30 542.75 5.41 542.74 6.21 542.76 R' 20.10 542.57 20.50 542.51 14.66 542.73 15.09 542.65 23.80 541.30 23.80 541.24 19.98 542.59 20.18 542.59 «• 29.50 541.02 TOBL BKFL 29.60 540.96 TOBL BKFL 23.53 541.30 23.71 541.22 32.90 539.61 31.30 540.34 26.44 540.93 27.35 541.03 3 { 36.00 539.40 39.20 539.30 42.90 539.26 33.00 33.40 TW 36.10 539.64 539.14 539.09 29.09 32.32 32.96 540.91 539.92 539.31 TOBL BKFI 29.74 32.33 33.87 540.88 539.82 539.16 TOBL BKFL TOE L 4 u e s v J1 45.90 539.29 48.20 539.47 37.80 38.90 538.98 538.47 35.92 38.49 539.25 538.73 TOE L 36.59 3821 539.19 538.78 50.10 539.68 41.30 538.40 TW 39.90 538.58 39.07 538.76 51.60 539.98 LOBRBKFF 42.80 538.42 43.14 538.44 TW 41.63 538.39 TW 54.40 541.11 45.70 538.49 47.21 538.60 46.73 538.82 60.30 541.36 62.30 542.52 48.00 49.90 538.67 539.01 49.50 50.39 538.65 539.68 TOE R 48.55 50.50 538.82 539.80 TOE R' Ar`' 69.30 542.78 51.90 539.86 52.52 540.26 52.65 540.18 76.70 543.18 RPIN 53.60 540.51 1 53.87 541.01 54.33 541.10 rOBR BKFR 55.00 540.87 rOBR BKFF 54.13 540.97 rOBR BKF 57.37 541.09 60.60 541.14 55.94 540.94 60.79 541.42 63.60 542.52 58.75 541.06 6220 542.47 71.70 542.84 60.44 541.46 65.96 542.66r_� _ 76.20 543.03 62.34 542.42 71.83 542.97 Photo of XS-2, looking In the downstream direction 76.70 543.23 RPIN 6625 542.68 76.31 543.08 71.59 542.89 76.64 643.18 RPIN 76.49 543.12 76.58 543.13 RPIN Cross Section 2 544.00 - 54x00 - 542.00 ILL. p 541.00 m W 540.00 539.00 538.00 0.00 10.00 20.00 30.00 40.00 50.00 60.00 70.00 80.00 90.00 Station (Feet) -+-As -Bust - (-Year 1 - .-Year 2 - a-Year 3 -+-BKF Project: McCain Property Summs bankfull Cross Section: Cross Section 3 MY3 MY4 MY5 MYO MYt MY2 Feature Pool Reach 2 A (BKF) 33.6 34.1 30.8 30.7 Station: 23.45.75 W (BKF) 22.6 23.0 22.3 22.1 Date: 8/25111 Max d 2.2 2.2 2.4 2.6 Crew: BW, ZAP, SV Mean d 1.5 1.5 1.4 1.4 W/D MY03.2011 MY00.2009 MY01 -2009 MY02 -2010 Station Elevation Notes Station Elevation Notes Station Elevation Notes Station Elevation Notes 537.42 LPIN 537.41 LPIN 537.42 LPIN _ 537.42 LPIN " 0.40 537.22 0.30 537.10 0.16 537.17 021 537.24 4.90 537.35 5.60 537.18 5.47 537.30 4.81 537.34 �5 A 10.80 537.23 10.70 537.06 10.85 537.15 9.33 537.27;- 14.80 536.00 15.30 535.76 TOBL BKFl 14.13 536.24 11.21 537.15 17.00 535.61 17.80 535.49 16.82 535.75 13.66 536.22 20.40 535.64 TOBLBKR 20.20 535.53 19.75 535.67 17.21 535.66 y .XSa -_ y ,'f ,:.;y w,,; 23.50 534.21 22.60 534.71 20.55 535.75 20.39 535.65 TOBL BKFL 24.80 534.18 25.30 534.23 20.59 535.67 TOBL BKFI 22.90 535.00 26.20 534.48 26.70 533.93 22.15 535.28 25.74 534.65 28.30 534.03 30.20 533.65 23.51 534.96 28.41 534.53 29.30 533.96 31.70 533.39 25.84 534.66 30.85 533.46 TOE L "< 33.50 533.72 33.90 533.39 27.64 534.57 33.36 533.03 TW 35.00 533.47 3620 533.49 29.25 534.26 35.53 533.29 35.70 533.43 TW 37.60 533.34 TW 29.91 533.73 TOE L 37.70 533.41 TOE R 37.80 533.51 39.40 533.90 31.73 533.51 39.46 534.12 ' 39.90 534.03 40.70 534.41 33.44 533.24 TW 42.27 535.48 43.90 536.10 rOBR BKF 44.60 536.11 rOBR BKF 35.66 533.40 45.16 536.37 rOBR BKFR 45.10 536.35 49.90 536.30 38.05 533.44 48.22 536.31' 50.00 536.45 53.40 537.72 38.48 533.49 TOE R 5024 536.56 56.60 539.15 56.90 539.05 39.52 534.06 53.15 537.77 60.80 539.51 62.70 539.47 42.28 535.18 57.12 539.19 :.. 64.70 539.76 RPIN 64.70 539.77 RPIN 44.41 536.24 rOBR BKF 61.55 539.63 45.35 536.32 64.93 539.74 Photo of XS -3 boldng in the downstream direction 47.78 536.29 64.94 539.74 RPIN 50.18 536.53 53.78 537.89 56.63 539.17 60.69 539.57 64.01 539.66 64.85 539.83 RPIN Cross Section 3 541.00 540.00 MOO 539.00 537.00 c yO 536.00 Ae m w 535.00 534.00 533.00 532.00 0.00 10.00 20.00 30.00 40.00 50.00 60.00 70.00 Station (Feet) tAS-BuiR -+~ Year 1 -*- Year 2 -w- Year 3 + BKF Project: McCain Property Summa bankfull Cross Section: Cross Section 4 MYO MYt MY2 MY3 MY4 MY5 Feature RHfle Reach 2 A (BKF) 30.5 29.7 31.3 30.3 Station: 25 +05.32 W (BKF) 23.3 23.4 24.4 24.3 Date: 8(25/11 Max d 1.8 2.0 2.1 2.0 Crew: Billy, ZAP, SV Mean d 1.3 1.3 1.3 1.2 W(D 17.4 18.4 19.1 19.5 MY03.2011 MYOO-2000 MY01.2009 MYO2.2010 Station Elevation Notes Station Elevation Notes Station Elevation Notes Station Elevation 536.96 Notes LPIN 536.98 [PIN 537.03 LPIN 536.96 LPIN 5.00 536.62 1.00 536.72 0.14 536.83 0.23 536.62 ' 11.40 536.32 4.90 536.57 7.07 536.48 5.72 536.56 18.80 535.00 9.80 536.21 14.93 536.07 11.25 536.27 23.90 534.73 TOBL BKFIL 14.40 536.09 16.99 535.36 15.98 536.05 27.90 533.01 16.30 535.79 1884 534.99 18.75 534.98 28.30 532.96 18.40 535.04 21.09 534.85 20.51 534.83 29.40 532.71 TW 19.50 534.82 24.04 534.62 TOBL BKFI 24.67 534.67 TOBL BKFL - 31.60 532.89 24.00 534.68 TOBL BKFL 26.40 533.67 27.38 533.45 33.60 532.94 27.00 533.34 27.45 533.25 28.91 532.51 34.80 532.81 28.50 532.52 28.30 532.55 TOE L 30.66 532.63 V' 37.20 532.76 29.30 532.54 30.05 532.64 33.36 532.48 TW 39.50 532.94 30.60 532.80 32.15 532.61 35.06 532.56 43.80 533.13 32.40 532.56 34.29 532.44 TW 36.68 532.80 TOE R 47.70 534.52 34.60 532.46 TW 35.57 532.61 41.65 533.62 49.30 534.51 IFOBR BKFF 37.00 532.74 37.56 532.76 TOE R 44.80 533.62 f x » 50.40 534.87 41.50 533.59 38.34 533.03 47.59 534.02 53.20 534.93 43.00 533.59 39.76 533.07 50.48 534.80 rOBR BKFR 58.70 536.66 44.70 533.49 41.03 533.43 53.81 534.94 65.90 536.65 46.00 533.70 1 42.30 533.59 57.03 536.13 69.40 536.72 RPIN 47.90 534.44 rOBR BKFF 44.75 533.51 58.87 536.53 50.50 534.82 45.77 533.63 69.44 536.54 54.00 535.03 47.37 534.37 69.69 536.63 RPIN 56.80 536.06 48.46 534.42 1 Photo of XS-4, IooWrg In the downstream direction 59.60 536.53 49.95 534.79 rOBR BKFR 66.20 536.62 52.78 534.80 69.40 536.70 RPIN 54.29 535.10 55.49 535.47 56.50 535.96 56.90 536.10 5893 536.48 62.10 536.53 69.35 536.50 69.47 536.59 RPIN Cross Section 4 538.00 537.00 535.00 yO 535.00 A W 534.00 533.00 532.00 0.00 10.00 20.00 30.00 40.00 50.00 50.00 70.00 80.00 SMIon (Feet) t A6 -Buit t Year 1 -.- Year 2 -0- Yew 3 -+- BKF Project: WCeln Property Summa bankfu0 - Cross Section: Goss Section 5 MYO MYt NIY2 MY3 MY4 MYS Feature Pool Reach 2 A (BKF) 22.2 17.8 20.5 18.7 Station: 29 +60.52 W (BKF) 16.7 14.3 16.0 14.0 Date: 8125/11 Max d 2.8 2.5 2.8 2.8 Crew: BW, ZAP, SV Mean d 1.2 12 1.3 1.3 WiD MYOO.2009 MY01.2009 MY02.2010 MY03.2011 Station Elevation Notes Station Elevation Notes Station Elevation Notes Station Elevation Notes 534.81 LPIN 534.83 LPIN 534.81 LPIN 534.81 LPIN 1.30 534.61 0.85 534.55 0.10 534.66 0.16 534.64 4.50 534.49 7.04 534.34 4.64 534.53 3.54 534.58 7.10 534.47 9.74 534.25 8.58 534.52 9.37 534.39 9.90 534.27 12.69 533.03 11.79 533.58 12.19 533.54 .a "- 15.60 532.08 15.31 532.09 14.13 532.51 16.43 531.84 22.10 531.29 TOBL BKFL 17.68 531.53 16.94 531.79 19.79 531.65 TOBL BKFL 23.50 530.57 21.06 531.28 TOBL BKFI 19.09 531.58 22.63 531.30 24.30 530.15 22.28 531.15 21.52 531.32 T08L BKFI 23.11 531.03 24.80 530.05 23.71 530.35 22.78 530.98 25.13 529.44 TOE L 26.10 528.48 TW 25.07 529.71 24.38 530.40 26.28 528.76 27.00 528.84 26.46 528.68 25.37 529.46 TOE L 27.09 528.53 TW 28.20 528.85 28.01 528.70 26.16 528.67 28.25 528.76 29.20 529.10 28.55 528.61 TW 27.85 528.46 TW 30.17 529.34 29.90 529.40 29.77 529.27 30.26 529.36 31.33 529.92 TOE R 31.00 529.75 30.71 529.72 31.96 529.68 TOE R 32.59 530.68 31.70 530.04 32.08 530.26 32.69 530.30 34.37 530.98 33.10 530.28 34.31 530.73 33.54 530.76 38.32 531.55 35.60 530.77 38.84 531.56 rOBR BKF 34.93 530.94 42.21 532.13 rOBR BKFR 38.60 530.66 42.10 531.99 37.34 531.25 43.68 532.24 42.30 532.07 rOBR BKFF 45.60 532.03 39.09 531.60 47.59 532.37 46.90 532.25 47.75 532.36 42.04 531.96 52.99 534.59 53.00 534.62 50.39 533.56 44.65 532.04 54.72 534.70 56.70 534.80 53.09 534.59 47.54 532.32 TOM BKF 59.47 534.88 Photo of XS-5, looking in the downstream direction 60.80 534.90 57.36 534.68 49.05 533.30 65.23 535.31 65.10 535.20 RPIN 61.80 534.85 50.87 533.82 65.25 535.30 RPIN 65.09 535.23 RPIN 53.22 534.64 57.43 534.76 61.37 534.89 64.64 535.11 64.92 535.11 RPIN Cross Section 5 536.00 535.00 534.00 533.00 532.00 p �W >t W 531.00 530.00 529.00 528.00 0.00 10.00 20.00 30.00 40.00 50.00 60.00 70.00 Station (Feet) -As-But - Year 1 -A- Year 2 t Year 3 t BKF Project: McCaln Property Summa bonkfutl Cross Section: Cross Section 6 M 1 MYt MY2 MY3 MY4 MYS Feature RUfle Reach 2 A (BKF) 30.8 25.2 27.8 28.1 Station: 31 +23.66 W (OKF) 20.6 18.4 20.8 20.6 Date: 8!25111 Max d 2.1 2.0 2.2 2.3 Crew: BW, ZAP, SV Mean d 1.5 1.4 1.3 1.4 WID 13.8 13.4 15.5 15.1 MY00.2009 MY01.2009 NrY02 -2010 MY03.2011 Station Elevation Notes Station Elevation Notes Station Elevation Notes Station Elevation Notes 534.05 IN 534.06 LPIN $34.05 LPIN 534.05 LPIN 1.20 533.88 0.70 533.82 0.46 533.87 0.21 533.90 6.30 533.79 6.70 533.62 3.65 533.88 3.74 533.84 12.00 532.04 11.40 532.13 6.56 533.73 8.24 533.32 18.40 531.79 27.20 531.57 TOBL BKR 19.30 27.10 531.73 531.56 TOOL BKR 9.79 12.11 532.77 532.09 11.43 16.28 532.21, 531.88 31.90 529.62 30.00 530.32 17.67 531.84 21.94 531.68 35.40 529.32 31.90 529.56 23.58 531.71 27.12 531.67 TOBL BKFL 37.20 529.17 35.50 529.56 25.48 531.75 29.67 530.68 y 39.20 529.13 TW 3720 529.46 27.37 531.63 TOBL BIKFI 32.05 530.04 41.30 529.29 39.00 529.10 29.66 530.59 35.18 529.78 43.10 529.25 40.30 528.98 TW 31.44 530.13 38.76 529.38 TOE L 43.70 529.27 44.30 529.66 41.60 43.80 529.06 529.14 32.62 35.86 529.76 529.59 TOE L 41.56 43.06 529.14 529.00 TW 48.60 531.25 rOBR BKF 44.70 529.74 37.90 529.44 44.22 529.13 TOE R 53.70 531.47 46.80 530.99 39.28 529.27 46.05 530.54 57.90 533.34 48.90 531.22 rOBR BKF 41.25 529.31 47.47 531.15 60.00 533.68 53.90 531.45 43.16 529.12 TW 49.15 531.36 rOBR BKFR 65.80 533.81 56.60 532.70 44.05 529.34 TOE R 51.66 531.41 67.80 534.22 RPIN 58.60 533.50 44.57 530.01 54.75 531.69 63.50 533.69 45.87 530.55 56.72 532.65 67.40 533.93 47.21 531.14 58.73 533.56 67.70 534.23 RPIN 50.46 531.45 rOBR OKF 6286 533.76 54.62 56.73 531.68 532.93 67.76 67.85 534.04 534.24 RPIN Plato of XS-6, looking in the downstream direction 58.82 533.61 60.49 533.81 63.53 533.88 67.45 534.10 67.46 534.26 RPIN Cross Section 6 535.00 534.00 7� 533.00 - 53200 C 531.00 W 530.00 - Af/ 529.00 528.00 0.00 10.00 20.00 30M 40.00 50.00 60.00 70.00 60.00 SWUM (Feet) --o- As -Built Year 1 -.- Year 2 --m- Year 3 -4o- BKF Elevation (feet) CA N W W ASP C C (A O () I O C11 p ROCK STRUCTURE 1 STA 10 +18 r 1 1 � 1 .l om 11 n � 11 N 1 C j CROSS SErTION 1 1 12 +11 ROCK E TRUCTURE OMMEMEdW cj STA 12+49 1 + O 1 � 1 O ' I O 1 Ln 1 + O O ROCK STRUCTURE1 p) STA 15 +5 D ' 1 + CD 1 11 CROSS SECTION 2 16 +25 1 1 V + I °0 1 1 + O O 1 ROCK STRUCTURE 1 O co STA IS -62 + O O O � 1 1 i N 1 O 1 O 1 1 0;1 1 7 i 1 + O r 0 I N 1 S C N m ' 0 1 N fp . 1 1 D W m i 7 7 a N� +O 1 ID O 11 1 COl 3 I( n + Q O� 23+46 0 1 Cw11 � O ROCK STRUCTU E 1 Ul STA 24+41 1 O O W + It CROSS SECTION 4 O 25 +05 O 1 tT G V) 0 1 O 1 V O W +O 1 1 0 1 1 co A I + O O co 1 W O 1 1 O 1 CROSS SECTION 5 W O 29+61 o ROCK 11 O STRUCTURE W STA 3 74 1 1 O 1 CROSS SECTION 6 O 31 +24 N 1 + °0 1 W I W I + O � 1 O 1 � ROCK11 + O O STA 3 +4 1 1 W 1 O O 1 PEBBLE COUNT Project: McCain Property Date: 8/25/2011 Location: Cross Section #1 Particle Counts Inches Particle Millimeter 32.9 Riffles Pools Total No. Item % % Cumulative 90% Silt/Clay < 0.062 5 /C:::: 0 0 0 0% 0% Very Fine .062-.125 ::: ; : =::: 0 0 0 0% 0% Fine .125-.25 : fk :::: 2 0 2 2% 2% Medium .25-.50 :: N :w::: 0 0 0 0% 2% Coarse .50-1.0 ::: D :::: 2 0 2 2% 4% .04-.08 1 Very Coarse 1.0-2.0 ::: S :::: 5 1 0 5 5% 9% .08-.16 Very Fine 2.0-4.0 0 0 0 0% 9% .16-.22 Fine 4.0-5.7 ::::G:: _ : _ 2 0 2 2% 11% .22-.31 Fine 5.7-8.0 ::::Fi::::::: 10 0 10 10% 21% .31-.44 Medium 8.0-11.3 A : :: 2 0 2 2% 23% .44-.63 Medium 11.3-16.0 V::::::: 8 0 8 8% 31% .63-.89 Coarse 16.0-22.6 :::::B::::: 10 0 10 10% 41% .89-1.26 Coarse 22.6 - 32.0 ::::::::::: 8 0 8 8 0/0 49% 1.26 - 1.77 Very Coarse 32.0-45.0 :S::::::::: 14 0 14 14% 63% 1.77-2.5 Very Coarse 45.0-64.0 14 0 14 14% 77% 2.5-3.5 Small 64-90 ::::: 10 0 10 10% 87% 3.5-5.0 Small 90-128 4 4 0 4 4% 91% 5.0-7.1 Large 128-180 ::$::: 6 0 6 6% 97% 7.1 - 10.1 Lar a 180-256 : L :::: 2 0 2 2% 99% 10.1 - 14.3 Small 256-362 B :::: 1 0 1 1 % 100% 14.3-20 Small 362-512 L :::::: 0 0 0 0% 100% 20-40 Medium 512-1024 D:: 0 0 0 0% 100% 40-80 L[ q- Very Lrq 1024-2048 :::: R :::: 0 0 0 0% 100% Bedrock BDFiI<:: j 0 0 0 0% 100% Totals 100 0 100 100% 100% d16 d35 1 d50 d84 d95 7.0 18.4 32.9 82.2 162.7 Bed Particle Size Distribution Cross Section 1: Riffle 100% 90% 80% d 70% W 0 MY -00 60%- E V 3 MY -01 50% C —6 MY -02 p 40% —�- MY -03 m LL 30% Ole 20% 10% 0% 0.1 1 10 100 1000 10000 100000 Particle Size - Millimeter PEBBLE COUNT Project: McCain Property Date: 8/25/2011 Location: Cross Section #2 Particle Counts Inches Particle Millimeter 157.7 Riffles Pools Total No. Item % % Cumulative 90%i° Silt/ Cla < 0.062 S/C ::: 4 0 4 4% 4% Very Fine .062-.125 ::: :::: 0 0 0 0% 4% Fine .125-.25 : tk :::: 0 0 0 0% 4% Medium .25-.50 N 0 0 0 0% 4% Coarse .50-1.0 0 0 0 0% 4% .04-.08 Very Coarse 1.0 - 2.0, :::: 15 0 15 15% 19% .08 - .16 Very Fine 2.0-4.0 0 0 0 0% 19% .16-.22 Fine 4.0-5.7 :(a:::: ': 2 0 2 2% 21% .22-.31 Fine 5.7-8.0 :R::::: 4 0 4 4% 25% .31 -.44 Medium 8.0 - 11.3 0 0 0 0% 25% .44-.63 Medium 11.3 - 16.0 V :::: 8 0 8 8% 33% .63-.89 Coarse 16.0-22.6 ::E:::,:. 13 0 13 13% 46% .89-1.26 Coarse 22.6-32.0 L:::: 4 0 4 4% 50% 1.26 - 1.77 Very Coarse 32.0-45.0 17 0 17 17% 67% 1.77-2.5 Very Coarse 45.0 - 64.0 20 0 20 20% 87% 2.5-3.5 Small 64-90 ::—::C. 2 0 2 2% 89% 3.5-5.0 Small 90-128 0: :: 2 0 2 2% 91% 5.0 - 7.1 Large 128-180 8:::::::: 7 0 7 7% 98% 7.1 - 10.1 Large 180-256 L: :::.:: 1 0 1 1 % 99% 10.1 -14.3 Small 256-362 B 1 0 1 1% 100% 14.3-20 Small 362-512 L 0 0 0 0% 100% 20-40 Medium 512-1024 D 0 0 0 0% 100% 40-80 Lr - Very Lrg 1024-2048 R 0 0 0 0% 100% Bedrock BDRK 0 0 0 0% 100% Totals 100 0 100 100% 100% d16 d35 d50 d84 d95 1.8 16.9 32.0 61.2 157.7 Bed Particle Size Distribution Cross Section 2: Riffle 100% 90%i° 1 80%i° 70% --0 MY -00 60% -:? - MY -01 50% MY -02 �o F 40% 40, MY-03 m A 30% LL 0 ° 20% 10% 0% 0.1 1 10 100 1000 10000 100000 Particle Size - Millimeter PEBBLE COUNT Project: McCain Property Date: 8/25/2011 Location: Cross Section #3 Particle Counts Inches Particle Millimeter 43.1 Riffles Pools Total No. Item % % Cumulative Silt/Clay < 0.062 S /C::: -: 12 12 12% 12% Very Fine .062-.125 ::: =R . : =: 0 0 0% 12% Fine .125-.25 ::: A :::: m 70% 2 2 2% 14% Medium .25-.50 =N :::: 0 0 0% 14% Coarse .50-1.0 :::::R :*... 0 0 0% 14% .04-.08 Very Coarse 1.0-2.0 S :::: E 0 0 0% 14% .08-.16 Very Fine 2.0-4.0 60% V 0 0 0% 14% .16-.22 Fine 4.0-5.7 : 50% 0 0 0% 14% .22-.31 Fine 5.7-8.0 :.:.:R...... C 0 0 0% 14% .31 - .44 Medium 8.0-11.3 : A :::: 40% 2 2 2% 16% .44-.63 Medium 11.3-16.0 : V :::: L 6 6 6% 22% .63-.89 Coarse 16.0-22.6 :::::::::: 10 10 10% 32% .89-1.26 Coarse 22.6-32.0 ::::::ir::::: 6 6 6% 38% 1.26 - 1.77 Very Coarse 32.0-45.0 14 14 14% 52% 1.77-2.5 Very Coarse 45.0-64.0 14 14 14% 66% 2.5-3.5 Small 64-90 G ::::: 6 6 6% 72% 3.5-5.0 Small 90-128 0::::: 8 8 8% 80% 5.0-7.1 Large 128-180 ::B:: 0 0 0% 80% 7.1 - 10.1 Lar a 180-256 L : :: 0 0 0% 80% 10.1 - 14.3 Small 256-362 B :::: 0 0 0% 80% 14.3-20 Small 362-512 : L :: 0 0 0% 80% 20-40 Medium 512-1024 :::D::::: 0 0 0% 80% 40-80 Lr - Very Lrg 1024-2048 R : :: 0 0 0% 80% Bedrock BOFiK:: 20 20 20% 100% Totals 0 100 100 100% 100% d16 d35 d50 d84 d95 11.0 27.0 43.1 1 0.0 0.0 Bed Particle Size Distribution Cross Section 3: Pool 100% 90% 80% m 70% 0 MY -00 E 60% V —2— MY -01 50% C 6 MY -02 40% MY -03 L d LL 30% ae 20% �:� 10% ,344�� 0% 0.1 1 10 100 1000 10000 100000 Particle Size - Millimeter PEBBLE COUNT Project: McCain Property Date: 8/25/2011 Location: Cross Section #4 Particle Counts Inches Particle Millimeter Riffles Pools Total No. Item % % Cumulative -Silt/Clay < 0.062 S /C::: -: 6 6 6% 6% Very Fine .062 - .125 : S :: 0 0 0% 6% Fine .125-.25 ::: A :::: 2 2 2% 80/0 Medium .25-.50 ::: PI :::: 0 0 0% 8% Coarse .50-1.0 : D :: 0 0 0% 8% .04-.08 1 Very Coarse 1.0-2.0 S :::: 0 0 0% 8% .08-.16 Very Fine 2.0-4.0 0 E 0 0% 8% .16-.22 Fine 4.0-5.7 :::::G:::::::: 4 4 4% 12% .22-.31 Fine 5.7-8.0 ::::R::::: 10 10 10% 22% .31 - .44 Medium 8.0 -11.3 ::A:::::::: 10 10 10% 32% .44-.63 Medium 11.3-16.0 : V : :: 4 4 4% 36% .63-.89 Coarse 16.0-22.6 :::::::::::::::: 0 0 0% 36% .89-1.26 Coarse 22.6-32.0 :::::L::::: 20 m 20 20% 560/6 1.26 - 1.77 Very Coarse 32.0-45.0 ::: =S :::: 10 10 10% 66% 1.77-2.5 Very Coarse 45.0-64.0 6 6 6% 72% 2.5-3.5 Small 64-90 6 6 6% 78% 3.5-5.0 Small 90-128 ::t7:::;::::: 15 15 15% 93% 5.0-7.1 Large 128-180 ::::B =: 0 0 0% 93% 7.1 - 10.1 Lar a 180-256 ::: L :: 2 2 2% 95% 10.1 - 14.3 Small 256-362 : B:::::::: 2 2 2% 97% 14.3-20 Small 362-512 :f :::::::: 0 0 0% 97% 20-40 Medium 512-1024 :::D::::: 0 0 0% 97% 40-80 L[ q- Ve LE9 1024-2048 ::::::::R::::::::: 0 0 0% 97% Bedrock ;:BQfiK:::: 3 1 3 3% 100% Totals 100 0 100 100% 100% d16 d35 d50 d84 d95 6.8 14.8 29.0 105.2 256.0 Bed Particle Size Distribution Cross Section 4: Riffle 100% 90% B El B E3 80% .. d 70% E 60% - 0 MY -00 9 B MY -01 50% W 40% —6 MY -02 - 0 MY -03 m 30% ii 3e 20% 10% 0% 0.1 1 10 100 1000 10000 100000 Particle Size - Millimeter PEBBLE COUNT Project: McCain Property Date: 8/25/2011 Location: Cross Section #5 Particle Counts Inches Particle Millimeter 16.9 Riffles Pools Total No. Item % % Cumulative 90% Silt/Clay < 0.062 S /C:::: 4 4 4% 4% Very Fine .062-.125 : S :::: 0 0 0% 4% Fine -125-.25 ::::A :: 0 0 0% 4% Medium .25-.50 ::::N :::: 0 0 0% 4% Coarse .50-1.0 : D :::: 0 0 0% 4% .04-.08 Very Coarse 1.0-2.0 4 4 4% 8% .08-.16 Very Fine 2.0-4.0 0 0 0% 8% .16-.22 Fine 4.0-5.7 Ea:: 4 4 4% 12% .22-.31 Fine 5.7-8.0 E 12 12 12% 24% .31 - .44 Medium 8.0-11.3 A : :: 12 12 12% 36% .44-.63 Medium 11.3-16.0 V :::: 12 12 12% 48% .63-.89 Coarse 16.0-22.6 :::::E::::: 14 14 14% 62% .89-1.26 Coarse 22.6-32.0 :::::L::::: 12 12 12% 74% 1.26 - 1.77 Very Coarse 32.0-45.0 : =S 6 6 6% 80% 1.77-2.5 Very Coarse 45.0-64.0 m LL 30% 8 8 8% 88% 2.5-3.5 Small 64-90 C :::: 4 4 4% 92% 3.5-5.0 Small 90-128 O : 0 0 0% 92% 5.0-7.1 Large 128-180 B : 0 0 0% 92% 7.1 - 10.1 Lar a 180-256 : L : 0 0 0% 92% 10.1 - 14.3 Small 256-362 B :::: 0 0 00/0 92% 14.3-20 Small 362-512 ::::: 0% 0 0 0% 92% 20-40 Medium 512-1024 :::::D::::: Particle Size - Millimeter 0 0 0% 92% 40-80 L[ q- Ve L[q, 1024 - 2048 :::: R :::: 0 0 0% 92% Bedrock B RK:: ........... 8 8 8% 100% Totals 0 100 100 100% 100% d16 d35 d50 d84 d95 6.7 10.8 16.9 54.5 0.0 Bed Particle Size Distribution Cross Section 5: Pool 100% 90% 80% .. d 70% W 7 $ MY -00 E v 60% -B- MY -01 C 50% 40% -6 MY -02 -0 -MY -03 m LL 30% 3e 20% 10% 0% 0.1 1 10 100 1000 10000 100000 Particle Size - Millimeter PEBBLE COUNT Project: McCain Property Date: 8/25/2011 Location: Cross Section #6 Particle Counts Inches Particle Millimeter 26.0 Riffles Pools Total No. Item % % Cumulative Silt/Clay < 0.062 :S /C::::: 3 3 6% 6% Very Fine .062-.125 :::: :: 0 80% 0 0% 6% Fine .125-.25 :::: 0 0 0% 6% Medium .25-.50 : KI :::: 0 0 0% 6% Coarse .50-1.0 : R :::: 0 0 0% 6% .04-.08 Very Coarse 1.0-2.0 ::: S :::: 2 2 4% 10% .08-.16 Very Fine 2.0-4.0 0 0 0% 10% .16-.22 Fine 4.0-5.7 ::::G:::::::: 2 2 4% 14% .22-.31 Fine 5.7-8.0 ::Fi::::: 5 5 10% 24% .31-.44 Medium 8.0-11.3 :::::i4::::::::: 2 2 4% 28% .44-.63 Medium 11.3-16.0 V :::: 4 4 80/a 36% .63-.89 Coarse 16.0-22.6 :::::::::::::::: 5 5 10% 46% .89-1.26 Coarse 22.6-32.0 :::::L::::: 5 5 10% 56% 1.26 - 1.77 Very Coarse 32.0-45.0 ::: S := :: 7 7 14% 70% 1.77-2.5 Very Coarse 45.0-64.0 10 10% 10 20% 90% 2.5-3.5 Small 64-90 C :::::: 5 5 10% 100% 3.5-5.0 Small 90-128 C7::::: 0 0 0% 100% 5.0-7.1 Large 128-180 ::::8:::::: 0 0 0% 100% 7.1 - 10.1 Larcle 180-256 :::: L :::: 0 0 0% 100% 10.1 - 14.3 Small 256-362 : B :::: 0 0 0% 100% 14.3-20 Small 362-512 :::::: ; :::::: 0 0 0% 100% 20-40 Medium 512-1024 :::::D::::: 0 0 0% 100% 40-80 L[ g- Ve Lrj 1024-2048 :::::::::R::::::::: 0 0 0% 100% EE Bedrock BIQf K:::: 0 0 0% 100% Totals 50 0 50 100% 100% ......... .... - --- d16 d35 d50 d84 d95 6.4 15.4 26.0 58.3 77.0 Bed Particle Size Distribution Cross Section 6: Riffle 100% 90% 80% d E 60% 0 MY -00 �j B MY -01 50% e 40% - MY -02 �— MY -03 m LL 30% 20% 10% 0% 0.1 1 10 100 1000 10000 100000 Particle Size - Millimeter Table 10a. Baseline Stream Data Summary McCain Stream Restoration Site/Project No. 443 - Reach: 1 286 feet Parameter Gauge Regional Curve Pre-Existing Condition Reference Reach es Data Design Monit"oring Baseline Dimension and Substrate • LL UL Eq. Min Mean Med Max SD' n Min Mean Mod Max SD' n Min Mod Max Min Mean Med Max SD' n Bankfull Width (ft) 14.6 18.7 25.9 29.3 4 10.4 27.1 18 16.9 Floodprone Width (ft) 34 95 125 125 3 150 200 35 Bankfull Mean Depth (ft 1.1 1.4 1.4 1.7 4 0.8 1.5 1.4 1.1 'Bankfull Max Depth ft 1.7 2.7 2.8 3.5 4 IA 2 2 1.5 Bankfull Cross Sectional Area ft2 21.3 25.6 25.9 29.3 4 12.5 22.3 24.6 18.6 Width /Depth Rati 8.3 14 15 17.6 4 11.6 18.5 13.2 15.4 Entrenchment Rati 1.8 5.6 6.4 8.5 3 7.4 14.4 2.1 'Bank Height Rati 1 1.2 1.1 1.7 4 1 1 1 1 Profile Riffle Length (ft) 9 108 58 54 63 63 72 12 2 Riffle Slope (ft/ft) 0.01 0.0756 0.0068 0.0048 0.0059 0.0059 0.007 0.0016 2 Pool Length (ft) 28 108 38 16 21 22 25 4 3 Pool Max depth (ft) 1.8 3.1 3 Pool Spacing (ft) 38 181 95 107 113 113 119 8 2 Pattern Channel Beltwidth (ft)i 75 135 78 Radius of Curvature (ft)l 14.5 26.8 30 35 35 38 38 40 2 Rc:Bankfull width (ftJft)l 1 1.6 1.7 1.9 2.1 2.2 2.2 2.4 Meander Wavelength (ft)l 70 148 190 204 1 Meander Width Ratij 3.6 13 4.6 Transport Parameters Reach Shear Stress (competency) Ib /f Max part size (mm) mobilized at bankfull Stream Power (transport capacity) W/m Additional Reach Parameters Rosgen Classification B4c /E4/C4 -5 B4c'C3'C4 B4c Bac Bankfull Velocity (fps) 3.9 Bankfull Discharge (cfs) Valley length (ft) 2155 Channel Thalweg length (ft) 2475 285 286 Sinuosity (ft) 1.15 1.50 -1.70 1.17 1.3 Water Surface Slope (Channel) (ft/ft) 0.0070- 0.0120 0.0067 0.0068 BF slope (ft/ft) 0.0070- 0.0120 0.0067 0.0065 'Bankfull Flood lain Area acres '% of Reach with Eroding Bank Channel Stability or Habitat Metric Biological or Othe bosom enua romewe ma, ,nc.e w,n,yp�auy „« � bum m. I = The dja I mina W ihmparampen em inebdc inf ,ion hm, bob da; crow.ms --ya and du: k v dkaf pm8k. ? = Faprojicia whh a prouna1 U3G3 gorge n -fne whh d,epmjxi reach faddcd henklull .vil" "cation ran:l. 1. IAtliring survey dau produce an uaimne of dlebankfull Ihiodphdn ama in aaa. wheh dw,M be Ne ana f the uy ofbanh m d,c Inc afdc mns rhvhlapa. 4 =Pmpmim nfrnch eab'bilh,g bmkn du, arc �rodmg br dm,hc riaW ��rmy fwcunpariaon mmoe,norhlg dau; S.Of vakdnpdod mhif dicn uc�a3 S'da ttna indlcau that thuc win lypeally na M filled in. I = The d- budone Im th- p.- aan meWde ml'amutbn hum buJi do noaa -ww, au ,and the Imgiudmal pm1i4•. 2 = Fn projsu wkh a pma W USGS gauge m -F , wish the pm}xt rush Wdw bankl'ull nmr dm J. lhilidng annoy dau produce an aatima�v or the Ean41u11 noodpmm aru in ancv. which ahouW be me w I'mm the wP nl hm�4 m tug d the urruc riuzMlapt•.. S = Protxmion ol'ruch cahibitmg Mn4a Net em cradi� hq� on the WauJ aor.<y Ihr eumpariaon m mmiming dau; d.01 raWGnadod only il'dtc n axeuda l Table 10a. Baseline Stream Data Summary McCain Stream Restoration Site /Pro ect No. 443 - Reach: 2 2184 feet Parameter I Gauge Regional Curve Pre-Existing Condition Reference Reach es Data Design Monitoring Baseline Dimension and Substrate - LL UL Eq. Min Mean Med Max SD' n Min Mean Med Max SD' n Min Med Max Min Mean Med Max SD' n Bankfull Width (ft) 14.6 18.7 25.9 29.3 4 10.4 27.1 18 20 24 20.6 22.8 23.3 24.6 0.9 3 Floodprone Width (ft) 34 95 125 125 3 150 200 47 54 51 63 6.2 3 Bankfull Mean Depth (ft) 1.1 1.4 1.4 1.7 4 0.8 1.5 1 1.3 1.4 1.3 1.4 1.4 1.5 0.1 3 'Bankfull Max Depth ft 1.7 2.7 2.8 3.5 4 1.4 2 1.3 1.7 2 1.8 1.9 1.8 2.1 0.2 3 Bankfull Cross Sectional Area ft2 21.3 25.6 25.9 29.3 4 12.5 22.3 25 25.5 26 30.8 31.89 31.2 33.7 1.3 3 Width/Depth Rat' 8.3 14 15 17.6 4 11.6 18.5 12.7 15.6 23 13.8 16.4 17.4 18 0.8 3 Entrenchment Rab 1.8 5.6 6.4 8.5 3 7.4 14.4 2 2.3 2.5 2.5 0.1 3 Bank Heigh Rat' 1.2 1.1 1.7 4 1 1 1 1 1 1 1 0 3 Profile Riffle Length (ft) 9 108 59 67 88 20 68 76 97 23 13 Riffle Slope (ft/ft) 0.01 0.0756 0.008 0.008 0.0104 0.0028 0.0087 0.0075 0.019 0.004 13 Pool Length (ft) 28 108 47 52 59 12 22 23 33 6 13 Pool Max depth (ft) 1.8 3.1 2.3 2.8 3.3 2.2 2.5 2.8 2 Pool Spacing (ft) 38 181 106 118 147 56 117 123 150 25 12 Pattern Channel Beltwidth (ft)l 75 135 20 62 97 24 10 Radius of Curvature (ft) 14.5 26.8 35 60 35 43 80 14 12 Rc:Bankfull width (fUft) 1 1.6 1.8 3.1 1.5 L221 2.2 3.3 Meander Wavelength (ft 70 148 212 236 294 158 229 261 36 10 Meander Width Rat 3.6 13 1.9 2.7 4.8 ransport Parameters Reach Shear Stress (competency) Ib/ Max part size (mm) mobilized at bankful Stream Power (transport capacity) W/m Additional Reach Parameters Rosgen Classification B4c /E4/C4 -5 B4c /C3 /C4 B4c 134c Bankfull Velocity (fps) 3.9 Bankfull Discharge (cfs) Valley length (ft) 2155 Channel Thalweg length (ft) 2475 285 286 Sinuosity (ft) 1.15 1.50 -1.70 1.17 1.3 Water Surface Slope (Channel) (ft/ft) 0.0070 - 0.0120 0.0067 0.0068 BF slope (ft/ft) 0.0070 - 0.0120 0.0067 0.0065 3Bankfull Flood lain Area acres a% of Reach with Eroding Ban Channel Stability or Habitat Metric Biological or Otherl S'da ttna indlcau that thuc win lypeally na M filled in. I = The d- budone Im th- p.- aan meWde ml'amutbn hum buJi do noaa -ww, au ,and the Imgiudmal pm1i4•. 2 = Fn projsu wkh a pma W USGS gauge m -F , wish the pm}xt rush Wdw bankl'ull nmr dm J. lhilidng annoy dau produce an aatima�v or the Ean41u11 noodpmm aru in ancv. which ahouW be me w I'mm the wP nl hm�4 m tug d the urruc riuzMlapt•.. S = Protxmion ol'ruch cahibitmg Mn4a Net em cradi� hq� on the WauJ aor.<y Ihr eumpariaon m mmiming dau; d.01 raWGnadod only il'dtc n axeuda l Table 10b. Baseline Stream Data Summary (Substrate, Bed, Bank, and Hydrologic Containment Parameter Distributions) McCain Stream Restoration Site /Project No. 443 - Entire Stream (2470 If) Parameter Pre-Existing Condition Reference Reach es Data Design As -built /Baseline 'Ri% /Rue/ /P % /G % /S% 56% 40%1 1 'SC % /Sa % /G % /C % /B % /Be% d16 /d35 /d50 /d84 /d95 /dF / di" (mm 2Entrenchment Class <1.5 / 1.5 -1.99 / 2.0-4.9 / 5.0 -9.9 / >1 #= Incision Class <12 / 1.2 -1.49 / 1.5.1.99 / >2. i —1-- ShaO et! cells IrOade Thal In—" lypicaly not be liled to I - Rigb, FM. Pod. Ciao, SW; SNt/Cky. Sand. Craw, Cobble, Barber, Baora *; alp- — pave, dsp . mar wbpeve 2. Entrenchment Clams - ! signibin the reach image into the cleses lndicaled erq p Wde the pace cage d the Taal ose,h Wage In each Gass n the lade This wll -neW Iran the measumd va:s-soclions as wet as ­W estimates 3 - Atssign/dn the neeeh loGNe ado the classes Indicated and prorvbe the percentage G the Idal reach IooltBe In eni less in the table. This A re%A horn the r eo ants- sectlms as vat es the bngfWmst prGnle Foolnoles ;9 - These Gasses 0-e lorsley bull awed the Reagan Gassftation and hmaa rig beeks, tae vrere aguslel shghhy to make for easier assipnmea to ser —her toes® inns basal m visual estinales n the Held such Thal measam 1 d eery segmcnl to ER wall nor be oneessary. The intent here's to Provide the readalcenshme of oesign a b mahhonrng in ooeellon with a good g dl save d the atoll d hy&dVc coolalnmenl'n the p—sisti g are the rehablhWw states as wet es canpansae to the nelsons dsh dons' ER and BHR have been aaoresseo n pna submsslons as a suhswoe (oose- sections as part of hle oes' f saucy). hoint— these shin —ples have dlen roc— sturdy on IacWaing design withwl pro idng o Ih—gh pre- conshulinn dstrhwlion G these pararrelas, k wft IM naaoerlcasana with a swig* Ihel is welghoo heaviy an the statee secgas G the reach. This means thal the dstndtions br these pe- nelers sho i hnkae data tron bUh the doss- section surveys orb the "Weal prattle and in the case of ER, visual enhnaes. For a nple. the typical kaghudnal pratle p000ds sampling d the SHR N Vies beyond these Wbjecl to soss-s ens and thedoe can be reeoly Megratetl art prwbe a more canylde sample dshiWion la these peen fors, themby pronong the c1stilbOion/caa9e reressery la peoMe meahrgtnl coo pe iso s. Table 1la. Monitoring Data - Dimensional Morphology Summary (Dimensional Parameters - Cross Sections) McCain Stream Restoration Site /Project No. 443 Cross Section 1 (Reach 1- Riffle) Cross Section 2 (Reach 2- Riffle) Cross Section 3 (Reach 2 -Pool) Based on fixed baseline bankfull elevation Base MY1 MY2 MY3 MY4 MY5 MY+ Base MY1 MY2 MY3 MY4 MY5 MY+ Base MY1 MY2 MY3 MY4 MY5 MY+ Record elevation (datum) us 544.4 544.3 544.4 544.4 541 540.9 541 541 535.6 535.5 535.6 535.6 Bankfull Width (ft 16.9 17.2 18.11 16.22 24.6 25.2 27.87 26.32 22.6 23 22.25 22.08 Floodprone Width (ft 35 37 35 35 63 >75 63 63 - - - - Bankfull Mean Depth (ft 1.1 1.2 1.033 1.096 1.4 1.7 1.584 1.645 1.5 1.5 1.384 1.388 Bankfull Max Depth (ft) 1.5 1.6 1 1.6 1 1.7 1 1 18 2.5 1 2.55 1 2.61 1 1 2.2 1 2.2 2.36 2.57 Bankfull Cross Sectional Area ft2 18.6 20.8 18.71 17.77 33.7 42.7 44.14 43.3 33.6 34.1 1 30.8 30.65 Bankfull Width /Depth Rati 15.4 14.2 17.52 14.79 18 14.9 17.59 16 - - - - Bankfull Entrenchment Rati 2.1 2.2 1.933 2.158 2.5 >3.0 2.261 2.394 Bankfull Bank Height Rati 1 1 1.1 1.188 1 1 0.969 0.954 Cross Sectional Area between end ins fe 174.2 182 184.8 184.21 119 137 137.4 136.91 97 87 90 167.3 d50 mm 21 1 18 1 13.5 1 32.9 19 17 1 24.2 1 32 8.1 1.7 31 43.1 Cross Section 4 (Reach 2- Riffle) Cross Section 5 (Reach 2 -Pool) Cross Section 6 (Reach 2- Riffle) Based on fixed baseline bankfull elevation Base MY1 MY2 MY3 MY4 MY5 MY+ Base MY1 MY2 MY3 MY4 MY5 MY+ Base MY1 MY2 MY3 MY4 MY5 MY+ Record elevation (datum) use 534.5 534.4 534.5 534.5 531.3 531.2 531.3 531.3 531.3 531 531.3 531.3 Bankfull Width (ft 23.3 23.4 23.99 24.32 18.1 14.3 16.46 13.96 20.6 18.4 20.79 20.6 Floodprone Width (ft) 47 52 47 47 51 50.5 51 51 Bankfull Mean Depth (ft) 1.3 1.3 1.234 1.246 1.2 1.2 1.282 1.339 1.5 1.4 1.339 1.363 Bankfull Max Depth (ft) 1.8 2 1.99 2.02 2.8 2.5 2.88 2.77 2.1 2 2.18 2.3 Bankfull Cross Sectional Area ft2 31.2 29.7 29.61 30.29 22.2 1 17.8 21.1 18.69 30.8 25.2 27.84 28.08 Bankfull Width /Depth Ratiol 17.4 18.4 19.44 19.53 - - - - 13.8 13.4 15.52 15.11 Bankfull Entrenchment Rati 2 2.2 1.959 1.932 2.5 2.7 2.453 2.476 Bankfull Bank Height Rati 1 1 1.095 1.084 1 1 1.069 1.026 Cross Sectional Area between end ins ftz 103 120 132.3 124.2 146 148 158.3 155.8 133 159 157.1 159.2 d50 mm 17 1 14 1 24 1 29 1 1 1 0.6 3 9.3 16.9 11 4.6 16.8 26 1 = Widths and depths for monitoring resurvey will be based on the baseline bankfull datum regardless of dimensional /depositional development. Input the elevation used as the datum, which should be consistent and based on the baseline datum established. If the performer has inherited the project and cannot acquire the datum used for prior years this must be discussed with EEP. If this cannot be resolved in time for a given years report submission a footnote in this should be included that states: "It is uncertain if the monitoring datum has been consistent over the monitoring history, which may influence calculated values. Additional data from a prior performer is being acquired to provide confirmation. Values will be recalculated in a future submission based on a consistent datum if determined to be necessary." 1 =The distributions-for these parameters can include information from both the cross - section surveys and Ife longitudinal profile. 2 = Proportion of reach exhbRirg barks that are eroding based on the visual survey from visual assessmern table 3 = Rifle, Run, Pool, Glide, Step: Silt/Clay, Sand, Gravel, Cobble. Boulder, Bedrock: dip = max pave, dlsp = max subpave 4. = Of value/needed orgy I the n exceeds 3 Exhibit Table 11 b. Monitoring Data - Stream Reach Data Summary McCain Stream Restoration Site /Project No. 443 - Reach: 1 286 feet Parameter Baseline MY -1 MY -2 MY- 3 MY- 4 MY- 5 Dimension and Substrate - Min Mean Med Max SD` n Min Mean Med Max SD" n Min IMean Med Max SD" n Min Mean Med Max SD` n Min Meanj Med I Max SD` n Min I Mean Med Max SD` n Bankfull Width (it) 16.9 17.2 17.03 16.22 Floodprone Width (it 35 37 35 35 Bankfull Mean Depth (ft 1.1 1.2 0.92 1.096 'Bankfull Max Depth k 1.5 1.6 1.42 1.7 Bankfull Cross Sectional Area lft' 18.6 20.8 15.67 17.77 Width/ Depth Rati 15.4 14.2 18.5 14.79 Entrenchment Pall 271 2.2 2.056 2.158 'Bank Height Rati 1 1 L239 1.188 Profile Riffle Length (ft)l 54.01 63.01 63.0172.01 12.01 2 1 1 67.01 1 50.46 54.87 54.87 59.27 6.23 2 43.86 49.61 49.61 55.36 2 Riffle Slope (ft4t 0.005 0.006 0.006 0.007 0.002 2 0.007 0.002 0.005 0.005 0.009 0.005 2 0.005 0.007 0.007 0.008 2 Pool Length (ft) 16.0 21.0 22.0 p25.0 4.0 3 25.0 30.0 31.0 93.02 96.96 96.96 100.9 5.57 2 28.85 63.2 58.56 102.2 36.88 3 Pool Max depth (ft 3.72 4.82 4.82 5.91 1.55 2 3.31 4.35 3.39 6.35 1.733 3 Pool Spacing (ft 107.0 113.0 113.0 119.0 8.0 2 112.0 125.0 194.0 127.1 1 104.5 117.9 117.9 131.4 2 Pattern Channel Beltwidth (ft 76 Radius of Curvature (ft 35 38 38 40 2 Rc:Bankfull width (ft!ft 2.1 2.2 2.2 2.4 Pattern data will not typically be collected unless visual data, dimensional data or profile data indicate significant shifts from baseline Meander Wavelength (ft 204 Meander Width Rati 4.6 dditional Reach Parameters Rosgen Classlficatlo B4c C4 B4c B4c Channel Thalweg length (ft 286 286 286 286 Sinuosity (ft 1.3 1.3 1.3 1.3 Water Surface Slope (Channel) (ft/ft} 0.0068 0..65 0.0074 0.008 BF slope (tt/f1) 0.0065 0.0039 0.0037 Ri% /Ru% /P% /G % /S% 38% t0% 47% 10% 34.69 5.619145.8118-2551 SC% /Sa % /G % /C % /B % /Be% 4% 19% 65% 11% 0% 1% 0% 9°/ 68% 22% 1% 0% dl 6 / d35 / d50 / d84 I d95 0.2 14.2 21.1 56.2 90 7 18 -4 32.9 82.2 162.7 of Reach with Eroding Bank t % 21% 9% Channel Stability or Habitat Metric Biological or Othe 1 =The distributions-for these parameters can include information from both the cross - section surveys and Ife longitudinal profile. 2 = Proportion of reach exhbRirg barks that are eroding based on the visual survey from visual assessmern table 3 = Rifle, Run, Pool, Glide, Step: Silt/Clay, Sand, Gravel, Cobble. Boulder, Bedrock: dip = max pave, dlsp = max subpave 4. = Of value/needed orgy I the n exceeds 3 Parameter Baseline MY -1 MY -2 MY- 3 MY- 4 MY- 5 Dimension and Substrate - Ritlle only Min Mean Mad Max SD° n Min Mean Mad Max SD` n Min Mean Mad Max SD° n Min Mean Mad Max SD' n Min Mean Med Max SD n Min Mean Mad Max SD° n Barddull Width (ft 20.6 22.8 23.3 24.6 0.9 3 18.4 22.33 23.4 25.2 3.523 3 20.79 23.08 23.99 24.44 1.992 3 20.6 23.75 24.32 26.32 2.904 3 Floodprone Width (ft 47 54 51 63 6.2 3 51 55.33 52 63 6.658 3 47 53.67 51 8.327 3 47 53.67 51 63 8.327 3 Baniffull Mean Depth (h 1.3 1.4 1.4 1.5 0.1 3 1.3 1.467 1.4 1.7 0.208 3 1.281 1.425 1.339 0.201 3 1.246 1.418 1.363 1.645 0.205 3 'Bankfull Max Depth h 1.8 1.9 1.8 2.1 0.2 3 2 2.167 2 2.5 0.289 3 2.06 2.197 2.18 0.146 3 2.02 2.31 2.3 2.61 0.295 3 Bardtfull Cross Sectional Area ftz 30.8 31.89 31.2 33.7 1.3 3 25.2 32.53 29.7 42.7 9.088 3 27.84 32.95 31.3 k1.069 6.102 3 28.08 33.89 30.29 43.3 8.222 3 Width/Depth Rati 13.8 16.4 17.4 18 0.8 3 13.4 15.57 14.9 18.4 2.566 3 14.5 16.37 15.52 2.41 3 15.11 16.88 16 19.53 2.335 3 Entrenchment Rati 2 2.3 2.5 2.5 0.1 3 2.2 2.467 2.5 2.7 0.252 3 1.923 2.334 2.453 0.366 3 1.932 2267 2.394 2476 0.293 3 'Bank Height Rati i 1 1 1 0 3 1 1 1 1 0 3 1.051 1.059 1.058 7009 3 0.954 1.021 1.026 1.084 0.065 3 Profile Riffle Length (ft 20.0 1 68.0 76.0 97.0 23.0 13 16.0 37.6 86.8 13.0 65.8 692 1112.0 29.3 17 15.63 74.41 69.7 196 37.61 17 Riffle Slope (" 0.003 0.009 0.008 0.019 0.004 13 0.001 0.012 0.027 0.002 0.011 0.007 0.059 0.013 17 0.000 0.005 0.006 0.011 0.003 16 Pool Length (h 12.0 122.0 23.0 33.0 CO 13 12.0 29.2 144.3 29.4 57.0 50.1 160.4 30.6 19 26.74 48.29 45.31 78.75 14.47 18 Pool Max depth (ft 2.2 2.5 2.8 2 1.8 3.1 2.8 5.9 0.9 19 2.15 3.372 3.405 4.43 0.655 18 Pool Spacing (ft 56.0 117.0 123.0 150.0 25.0 12 52.0 144.0 317.0 76.9 121.5 116.5 183.7 30.7 18 48.5 124.9 121 241.2 43.89 17 Pattern Channel Beltwidth (ft 20 66 62 97 24 10 Radius of Curvature (ftj 35 1 49 1 43 1 80 14 12 Rc:Bankfull width (ft/ft 1.5 22 2.2 3.3 lorel data or probe data indicate Pattern data will not typically be collected unless visual data, baseline significant shihs from baselne Meander Wavelength (ftj 158 1 221-1 229 1 261 36 10 Meander Width Ratiol 1.9 1 3.1-1 2.7 4.8 ddftional Reach Parameters Rosgen Classificatio C4 C4 C4 C4 Channel Thalweg length (ft 2182 2182 2182 2182 Sinuosity (h 1.18 1.78 1.18 1.18 Water Surface Slope (Channel) (ftRt 0.0068 n.0067 0.0066 0.0066 BF slope (ft4t 0.0065 0.007 0.0068 0.0063 1% /RU % /P % /G %/S 54% 2% 32% 16% 1 1% 2°/ 33% 5% 'SC%/Sa%/G%/C%/B 11% 10% 71% 7% 0% 1% 5% 7°/ 71% 15% 1 1% 1 1% dl6 / d351 d50 / d841 d95 1.6 6.22 14.06 41.34 97.76 5 15.68 29 74.88 163.6 a%of Reach with Eroding Bank 0% 1% 0% Channel Stability or Habitat Matti Biological or Othe �naoed cela indbate that these wa typxal y not oe haw in. 1 = The distribulons for these parameters can include Information from both the crass - section surveys and the longitudinal profila. 2 = Proportion of reach exhbtirg barks that are eroding based on the visual survey from visual assessmom table �I Appendix E. Hydrologic Data 1 McCain Stream Restoration Year 3 Monitoring Report NCEEP Project number 443 Year 3 of 5 Ward Consulting Engineers, P C December 2011 �J E Table 12 Verification of Banldull Events Table 12. Verification of Bankfull Events McCain Site Stream Restoration - Project No. 443 Date of Data Date of Collection Occurrence Method Photo # 17 -Nov -09 13- Nov-09 Site Visit to evaluate indicators of stage after storm events N/A Photo 14 30- Sep -10 30- Sep -10 NWS COOP Station and site visit for confirmation MY -02 Report No new bankfull events were observed or recorded by the onslte stream crest gauge prior to the W -03 data collection date (August 25, 2011) U 0 LI LI McCain Stream Restoration Year 3 Monitoring Report NCEEP Protest number 443 Year 3 of 5 Ward Consulting Engineers, P C December 2011