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,v Ihird Fork Creek Stream Restoration - NCEEP Project #139
Durham, North Carolina
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Caonnrl Annnal Mnnitnrina Rarinrf Tlaramhar 2(IfiA
4601 Six Forks Road
Raleigh, North Carolina 27609
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itted to:
North Carolina Department of Environment and
Natural Resources
Ecosystem Enhancement Program
1652 Mail Service Center
Raleigh, NC 27699-1652
Designed by:
KCI Associates of North Carolina, P.A.
Landmark Center II, Suite 220
I
THIRD FORK CREEK STREAM RESTORATION - NCEEP Project #139
2006 MONITORING REPORT - YEAR 2
CONDUCTED FOR THE NORTH CAROLINA DEPARTMENT OF ENVIRONMENT
AND NATURAL RESOURCES
Table of Contents
1. Executive Summary ....................................................................................................... .. 3
II. Project Background ................................................................................................... .. 3
A. Location and Setting ................................................................................................ .. 3
B. Structure and Objectives .......................................................................................... .. 4
C. History and Background ........................................................................................... .. 6
III. Project Conditions and Monitoring Results ................................................................ .. 9
A.Vegetation Assessment ............................................................................................. .. 9
1. Soil Data ............................................................................................................... .. 9
2. Vegetation Problem Areas ..................................................................................... 9
2.1. Upstream Reach ............................................................................................ 10
2.2. Downstream Reach ....................................................................................... 10
3. Stem Counts ......................................................................................................... 10
4. Vegetation Plot Photos ......................................................................................... 13
B. Stream Assessment .................................................................................................. 13
C. Wetland Assessment ................................................................................................ 22
LIST OF FIGURES
Figure 1 Vicinity Map ............................................................................... 5
Figure 2 Monitoring Plan View .....................................................................8
Figure 3. USGS Stream gauge data for Ellerbe Creek near Gorman, N.C ...................15
LIST OF TABLES
Exhibit Table I. Project Mitigation Structure and Objectives ....................................6
Exhibit Table II. Project Activity and Reporting History ...................................... ...6
Exhibit Table III. Project Contact Table .......................................................... ...7
Exhibit Table IV. Project Background Table .......................................................7
Exhibit Table V. Preliminary Soil Data ............................................................................. ....9
Exhibit Table VI. Vegetative Problem Areas .................................................................... ...9
Exhibit Table VII. Stem Counts for Each Species Arranged by Plot ................................. ...12
Exhibit Table VIII. Verification of Bankfull Events ......................................................... ...14
Exhibit Table X. Stream Problem Areas ........................................................................... ....16
Exhibit Table XI. Categorical Stream Feature Visual Stability Assessment .........................17
Exhibit Table XII. Baseline Morphology and Hydraulic Summary ................................... ...18
Exhibit Table XIII. Morphology and Hydraulic Monitoring Summary ............................. ...23
Third Fork Creek Stream Restoration 2006 Monitoring Report
EEP Project # 139 Year 2 of 5
RJG&A Page 1
APPENDICES
Appendix A Vegetation Raw Data
A-1 Vegetation Problem Area Plan View
A-2 Vegetation Problem Area Photo
A-3 Vegetation Survey Summary Data
A-4 Vegetation Monitoring Plot Photos
A-5 Vegetation Raw Data
Appendix B Geomorphologic Raw Data
B-1 Exhibit - Problem Areas Plan View
B-2 Representative Stream Problem Area Photos
B-3 Stream Photo-station Photos
B-4 Table B.1 Qualitative Visual Stability Assessment
B-5 Cross section Plots and Raw Data Tables
B-6 Longitudinal Plots and Raw Data Tables
B-7 Pebble Counts
Third Fork Creek Stream Restoration 2006 Monitoring Report
EEP Project #139 Year 2 of 5
RJG&A Page 2
I. Executive Summary
The Third Fork Creek stream restoration project is located in southwest-central Durham,
North Carolina, in the headwaters of the Third Fork Creek watershed (US Geological
Survey14-digit Hydrologic Unit Code 03030002060120) within the New Hope Creek
Sub-basin of the Upper Cape Fear River (NC Division of Water Quality Sub-basin 03-06-
05). The project has restored approximately 2,900 linear feet of perennial stream in the
Cape Fear River Basin. Evaluation and design were initiated during the summer of 2002.
Construction was completed in January 2005. The stream restoration project's goals
were: to restore stable channel morphology, which will reduce bank erosion; improve the
watershed's sediment transport; improve aquatic habitat diversity; and increase aesthetic
value to local stakeholders.
The preliminary qualitative evaluation was conducted by RJG&A in early February 2006.
Subsequent qualitative evaluation was conducted during early March, late June, and
September 2006. The second vegetation monitoring data were collected during
September 2006, using EEP's August 2006 monitoring protocol. The second annual
geomorphologic monitoring data were collected during October 2006.
Overall, the restoration project has met its design goals. Several major geomorphologic
changes were documented during the second monitoring year, but overall the site is
relatively stable. Aquatic and semi-aquatic organisms have colonized most of the
restoration area and the average live planted woody stem density (926 per acre) has
exceeded the vegetation restoration goal (320 per acre) by 289 percent.
II. Project Background
A. Location and Setting
The entire restoration site is contained within Forest Hills Park, which is owned by the
City of Durham. To get to the Third Fork Creek restoration site from NC 147, take exit
12B and travel south on Roxboro Road. Turn east on West Lakewood Avenue, which
merges into University Drive. Forest Hills Park and the Third Fork restoration site are on
the left (eastern) side of University Drive (US 151501 Business, Figure 1). The upstream
boundary of the restoration project is immediately downstream from where Third Fork
Creek emerges from the box culvert under the northern stretch East Forest Hills
Boulevard. The stream restoration extends downstream along the main channel from this
point to the southern edge of the Forest Hills Park. The double box culvert under the
southern stretch of the East Forest Hills Boulevard loop divides the restoration into upper
and lower reaches. An unnamed tributary to Third Fork Creek joins the lower reach on
the downstream end of the culvert. The lower reach therefore has a significantly larger
watershed.
Forest Hills Park is dominated by lawn/open space with relatively little mature canopy
cover (less than 25 percent). A playground and other facilities with impervious cover (e.g
swimming pool, tennis courts, and picnic shelter) are located near the southern portion of
the restoration's upper reach. The surrounding area is highly urbanized. The majority of
Third Fork Creek Stream Restoration 2006 Monitoring Report
EEP Project #139 Year 2 of 5
RJG&A Page 3
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Figure 1. Third Fork Stream
Restoration - Durham County, NC Islas.
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Third Fork Creek Stream Restoration 2006 Monitoring Report
EEP Project #139 Year 2 of 5
RJG&A Page 5
the land use is dedicated to residential and commercial development and secondary roads.
Prior to the restoration, both project reaches were incised and had active bed degradation
and channel widening characterized by severe bank erosion.
B. Structure and Objectives
A priority 2 stream restoration approach was used to design and reestablish
approximately 3,025 linear feet of meandering, bankfull channel and a new floodplain
along Third Fork Creek. The project restored riffle-pool sequencing and used cross-vane
and j-hook in-stream structures to provide grade control. The unnamed tributary that
enters from the upper reach's left bank (station 20+33) was incorporated and stabilized
with a grade control structure to match the grade of the restored channel. Coir fiber
matting and live staking were installed/planted to help stabilize the graded stream banks.
A 50 foot wide buffer was planted with native species on both sides the restored stream.
Space and use needs in the park limited the woody plantings to within 30 feet of the
stream. The buffers' outer twenty feet was planted in native grasses andis managed
(mowed).
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Third Fork Creek Stream Restoration 2006 Monitoring Report
EEP Project #139 Year 2 of 5
RJG&,A Page 4
Exhibit Table I. Mitigation Structure and Objectives - Third Fork Creek Stream Restoration - EEP
Project #139 - Durham, NC
Reach ID Mitigation Approach Linear Stationing Mitigation Comment
Type Feet Credits (ratio)
Upstream Restoration Priority 2 10+00-
26+00
o c3
Downstream Restoration Priority 2 N 25+00 -
40+25 M
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0
C. History and Background
Exhibit Table II. Activity and Reporting History - Third Fork Creek
Stream Restoration - EEP Project #139- Durham, NC
Activity or Report Data Collection Completion
Restoration Plan 2002 February 2003
Construction NA January 2005
Temporary S&E mix applied NA NA
Permanent seed mix applied NA NA
Bare Root Planting NA NA
Mitigation Plan NA December 2005
(report date
As-built March 2005 December 2005
(report date)
Year 1 Monitoring December 2005
(report date)
Vegetation September 2005
Geomo holo ical September 2005
Year 2 Monitoring December 2006
(re ort date)
Vegetation September 2006
Geomo holo ical October 2006
Third Fork Creek Stream Restoration 2006 Monitoring Report
EEP Project #139 Year 2 of 5
RJG&A Page 6
Exhibit Table III. Project Contacts - Third Fork
Creek Stream Restoration - EEP Project #139 -
Durham, NC
Design:
KCI Associates of North Carolina, P.A.
Landmark Center II, Suite 220
4601 Six Forks Road
Raleigh, North Carolina 27609
Mr. Joe Pfeiffer
919) 783-9214
Construction Contractor:
NA
Monitoring Performers:
RJG&A
1221 Corporation Parkway, Suite 100
Raleigh, NC 27616
Mr. Ward Marotti
919) 872-1174
Exhibit Table IV. Project Background - Third Fork Creek Stream - EEP Project #139
County Durham
Drainage Area 1,126.4 acres 1.76 square miles
Drainage Impervious Cover Estimate 44%
Stream Order Second Order
Ph sio ra hic Region Piedmont
Ecore ion Triassic Basins
Ros en Classification of As-built
Upper Reach F5, G5, E5
Lower Reach C5
Dominant Soil Types
Upstream Reach Congaree
Downstream Reach Congaree
Reference Site ID North Prong Creek
USGS HUC for Project and Reference 03030002060120, 0303002060140
NCDWQ Sub-basin for Project and Reference 03-06-05, 03-06-05
NCDWQ Classification for Project and
Reference C
An portion of the project segment 303d listed? Yes
Any portion of the project segment upstream of
a 303d listed segment? Yes
Reasons for 303d Listing or Stressor Turbidity, low dissolved oxygen, fecal coliform
bacteria
% of Project Easement Fenced 0%
Third Fork Creek Stream Restoration 2006 Monitoring Report
EEP Project #139 Year 2 of 5
RJG&A Page 7
Figure 2. Monitoring Plan View
Third Fork Creek Stream Restoration 2006 Monitoring Report
EEP Project #139 Year 2 of 5
RJG&A Page 8
• Figure 2.1 - 2006 Monitoring.
Plan View - Year 2
Third Fork Creek (Forest Hills)
Stream Restoration - Durham, NC
T TGXn ; LEGEND
-2006 Thalweg
2006 Vegetation Monitoring Plots
Cross Sections
S
S 0 w o0 ! Photopoints
As-built Drawings (Supplied by KCI)
Vanes
e o
--- Thalweg
N o -- Edge of water
+ S S -- Conservation Easement
Sewer ROW
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Easting Northing
Vegetation Plots
1 2026252.522400 812789.657666
2 2026222.941600 812569.691675
3 2025987.289460 812136.701257
4 2025961.194110 811689.362376
Cross-sections
1-L 2026045.167310 812046.165066
1-R 2026008.863870 812074.268999
2-L 2026019.907700 811829.907400
2-R 2025969. 1 14450 811842.610456
Photopoints
1 2026280.064630 812942.007941
2 2026245.292230 812638.539733
3 2026224.428790 812585.685687
4 2026034.128930 812393.109820
5 2026035.393380 812128.144141
6 2025987.976480 812046.207724
7 2025968.377490 811836.182435
8 2025926.650610 811606.368490
0
7qW
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Easting Northing
Vegetation Plots
5 2025825.804140 811325.105992
6 2025751.559070 810836.827402
7 2025773.300850 810651.892462
8 2025829.725470 810411.548741
Cross-sections
3-L 2025870.880914 810673.554871
3-R 2025770.851314 810650.406271
L
4-L 2025798.603914 810554.818971
m 4-R 2025759.096714 810575.310971
Photopoints
9 2025883.659280 811374.025644
10 2025782.503210 811250.741684
ll E 11 2025792.618820 811001.328751
12 2025781.870990 810914.081641
13 2025766.697570 810688.630051
14 2025800.837750 810416.773115
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Figure 2.2 - 2006 Monitoring.
Plan View - Year 2
Third Fork Creek (Forest Hills)
Stream Restoration - Durham, NC
LEGEND
----- 2006 Thalweg
® 2006 Vegetation Monitoring Plots
-?--? Cross Sections
Photopoints
As-built Drawings (Supplied by KCI)
Vanes
- Thalweg
-- -- Edge of water
Conservation Easement
Sewer ROW
III. Project Conditions and Monitoring Results
RJG&A initially evaluated the site during early February 2006. It was qualitatively
evaluated during and after significant storm events in April and May 2006, and during
low flow in late June, September, and October. Vegetation monitoring was performed
during September 2006, pursuant to the August 2006 EEP guidelines.
Structural failure and compromise were recorded in a number of specific locations.
Exotic invasive woody stem density is relatively low. Planted woody stem density is
high, as is success. Exotic invasive vines have had a moderate impact on planted woody
stem success on several floodplain benches
In spite of the problem areas the overall restoration project appears to be adequately
transporting urban sediment loads and restoring aquatic habitat (i.e. meeting its design
functions/goals).
A. Vegetation Assessment
1. Soil Data
Exhibit Table V. Preliminary Soil Data - Third Fork Creek Stream - EEP Project
#139 - Durham, NC
Series Max Depth % Clay on K T OM%
(in.) Surface
Congaree 80 7-27 0.37 5 0.5-2.0
2. Vegetation Problem Areas
Planted woody vegetation appeared to be successful when qualitatively evaluated during
September 2006. Invasive exotic woody species have colonized many locations but are
quite sparse, relative to the planted native woody stems. Invasive exotic vines have had a
detrimental impact to survival on several floodplain benches that have received overbank
flow several times during the 2006 growing season.
Exhibit Table VI. a etation Problem Ar s - Third Fork Creek Stream - EEP
Project #139 - Durham, NC
Feature/Issue Station/Range Probable Cause Photo #
Exotic Invasive Vines 12+75- 14+00 Colonization of floodplain by
waterborne seeds VP2&3
Exotic Invasive 12+75 -14+00 Colonization by air and water
Wood Stems
borne seeds VP4&5
Exotic Invasive vines 16+75 19+75 Colonization of floodplain by
waterborne seeds VP2&3
Exotic Invasive vines 20+75 -22+40 Colonization of floodplain by
waterborne seeds VP2&3
Exotic Invasive vines 24+60- 26+25 Colonization of floodplain by
waterborne seeds VP2&3
Third Fork Creek Stream Restoration 2006 Monitoring Report
EEP Project #139 Year 2 of 5
RJG&A Page 9
Exhibit Table VI. Vegetation Problem Areas - Third Fork Creek Stream - EEP
Project #139 - Durham, NC
Disturbed area 29+90 -30+80 Diseased tree removal by City of VPl
Durham maintenance crew
Woody invasives 34+20 -35+70 Colonization by air and water VP4&5
borne seeds
Invasive vines 36+60 -37+25 Colonization of floodplain by VP2&3
waterborne seeds
2.1. Upstream Reach
Planted woody stem success was high in the upstream reach. Japanese hops (Humulus
japonicus) and porcelainberry (Ampelopsis brevipedunculata) have densely colonized the
floodplain benches inside several meanders. In addition to directly competing for light
with the planted woody species, these exotic invasive woody vines have caused many of
the planted woody stems in these areas to be severely impacted by storm flow. Once
rooted, most woody stems can withstand moderate flood events (i.e. they are bent during
over-bank flow, but not uprooted. With a dense layer of woody vine stems wrapped
around and through them, many planted individuals are uprooted, overturned, and washed
away entirel Manual removal of these vines could be an effective management
e, if it is done regularly. If not, the vines will recolonize the floodplain benches
from existing root stock, or from the large monocultures of these species upstream
(on/over both banks throughout the American Tobacco Trail right-of-way (1,400 feet
upstream)).
\P1_ 2.2. Downstream Reach
The downstream reach also has invasive exotic woody vines inside one meander and
some exotic invasive woody species along a portion of one bank.
3. Stem Counts
Eight representative vegetation survey plots were selected and installed in the upstream
and downstream reaches during September 2006, pursuant to the new EEP vegetation
monitoring protocol (August, 2006). Where appropriate, the new monitoring plots were
co-located with the first year monitoring plots. Pursuant to the August 2006 protocol, all
plots measure 100 square meters in area and are either 10 meters by 10 meters, or five
meters by 20 meters. Level 1 (planted woody stems) and Level 2 (volunteer woody
stems) data collection was performed concurrently with plot selection, during September
2006. Because the new plot dimensions are different than the first annual vegetation
monitoring plots, direct comparison with the first year data is inappropriate.
Pursuant to the new guidelines, the four corners of each plot (e.g. 0,0; 0,10; 10,0; and
10,10; or 0,0; 0,20; 5,0; and 5,20.) were marked with 18 inch long one half inch diameter
galvanized steel conduit. Within each plot, each planted woody stem location (x and y)
was recorded and live stem diameter at decimeter height (ddm), and height (cm) were
recorded.
Third Fork Creek Stream Restoration 2006 Monitoring Report
EEP Project #139 Year 2 of 5
RJG&A Page 10
The average live, planted woody stem density for all plots was 22.88 individuals per plot,
which translates to 929.95 stems per acre. This exceeds the required 320 stems per acre
by 291 percent.
Third Fork Creek Stream Restoration 2006 Monitoring Report
EEP Project # 139 Year 2 of 5
RJG&A Page 11
Exhibit Table VII. Stem counts and summary data by species and plot - Third Fork Creek Stream - EEP Project #139, Durham County, NC
---------- Reach ----------
Unstream Downstream
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Albizia julibrissin 1 1 100 1.00 8.76 0.55 0 0 1
Alnus serrulata 17 17 100 2.43 11.67 9.29 0 0 3 1 6 1 1 3 2
Amelanchier arborea 1 1 100 0.13 23.97* 0.55 0 1.00 0 1
Betula nigra 12 12 100 1.50 13.35 6.56 0 1.71 0 2 1 2 1 3 2 1
Callicarpa americana 25 25 100 3.13 7.07 13.66 0 3.57 0 4 8 5 1 4 2 1
Cercis canadensis 2 2 100 0.25 14.64 1.09 0 1.00 0 1 1
Cornus amomum 16 16 100 2.00 11.29 8.74 0 2.00 0 4 3 2 1 2 2 1 1
Fraxinus pennsylvanica 23 23 100 2.88 8.16 12.57 0 3.83 0 3 3 2 1 12 2
Hamamelis virginiana 7 7 100 0.88 6.55 3.83 0 1.40 0 1 1 2 1 2
Ilex deciduas 4 4 100 0.50 7.07 2.19 0 1.00 0 1 1 1 1
Ilex opaca 4 4 100 0.50 12.52 2.19 0 1.33 0 1 2 1
Itea virginica 14 14 100 1.75 5.94 7.65 0 2.80 0 6 1 3 2 2
Morella cerifera 9 9 100 1.13 14.74 4.92 0 2.25 0 2 1 3 3
Platanus occidentalis 18 18 100 2.25 15.78 9.84 0 2.57 0 7 2 1 2 3 2 1
Salix nigra 2 2 100 0.25 LS 1.09 0 2.00 0 2
Sambucus canadensis 3 3 100 0.38 12.00 1.64 0 1.00 0 1 1 1
Symphoricarpos 17 17 100 2.13 5.95 9.29 0 2.12 0 1 3 5 2 1 3 1 1
orbiculatus
Viburnum dentatum 7 7 100 0.88 7.54 3.83 0 3.50 0 3 4
Viburnum nudum 1 1 100 0.13 3.60 0.55 0 1.00 0 1
Total planted woody 183 183 100 100 0 0 33 29 32 13 10 39 17 10
stems (all plots)
Average planted woody 926 1,336 1,174 1,295 526 405 1,578 688 405
stems per acre
Average all woody stems 1,2852 1,902 1,255 1,619 1,174 567 2,549 809 405
per acre
*DBH
Third Fork Creek Stream Restoration
EEP Project #139
2006 Monitoring Report
Year 2 of 5
RJG&A Page 12
4. Vegetation Plot Photos
Vegetation plot photos are in Appendix A.
B. Stream Assessment
RJG&A personnel initially evaluated the site during early February 2006. It was
qualitatively evaluated during and after significant storm events in April and May 2006,
and during low flow in late June, September, and October 2006. The second annual cross
section, pattern, and longitudinal profile data were collected during October 2006.
Markers for cross sections one and two were not re-located in the field, using a total
station and a metal detector. Their locations were established using total station survey
equipment and best professional judgment. While not in the identical location as the
monitoring year 01 and as-built cross sections, the Year 02 cross section locations are
within 20 feet, likely upstream. Because these locations provide representative stability
condition data very close to the year 1 and as-built, their comparison to the original data
is appropriate. Photographs were taken at the four cross sections and at the 14 permanent
photo locations that were established by KCI in March 2005.
Overall, the site is maintaining its as-built dimension, pattern, and profile, and planted
woody stem success is high. Several stretches of bank erosion are present in both
reaches. One of these (station 34+27) is fairly significant, and getting worse (i.e. it has
expanded laterally and longitudinally since February). Remedial action (e.g. armoring
with root wads and/or roc hould be considered. Overall, the remaining bank slumps
and underc relatively minor and should continue to be monitored, as they may
rate themselves over time. The only other significant problem area (i.e. remedial
\ action should be considered) is a backcut j-hook that has had its upstream-most header
rock undercut (station 27+04). The rock has been completely dislodged and fallen back
(upstream) into the scoured channel. The remaining j-hook/cross vane problem areas are
I relatively minor and should continue to be observed, to determine if remedial action
should occur.
(? A wetted perimeter bed material analysis was performed at each cross section during
October 2006. The difference between the second annual monitoring substrate analysis
and the first year's indicates that the upstream-most channel bed has become finer (xsl),
while the downstream-most bed (xs2-4) have become coarser. The most significant
change was observed at cross section 3.
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Tbird Fork Creek Stream Restoration 2006 Monitoring Report
EEP Project #139 Year 2 of 5
RJG&A Page 13
Two pressure transducers were observed
during the initial evaluation in February.
The serial numbers, brands and model
numbers were recorded. A Solinst
Levelogger 3001 reader was subsequently
purchased and installed into a laptop. The
laptop was brought to the site on 25 April
2006. The gauges had been removed from
the PVC crest gauge pipes that held them.
Neither gauge was found, after an
extensive search, including inside the
installed pipe. The upstream unit still had
its lock, the lower one had a broken top (above photo). The units are presumed to have
been removed by vandals. On-site hydrologic data are therefore not available for the
second annual monitoring. Qualitative evaluation (rack and drift lines and downed
herbaceous and woody vegetation on the floodplain) indicated at least three events during
2006 (April, June, and September (above photo)).
Potential bankfull events were also evaluated based on USGS stream gauge discharge
data for Ellerbe Creek near Gorman (USGS 02086849). This gauge is located
approximately 8 miles northeast of the restoration site and has a drainage area of 21.9
square miles. According to the urban piedmont regional curve, a stream with a drainage
area of 21.9 square miles would reach a bankfull discharge at 2,144.5 cubic feet per
second (cfs) (Doll et al., 2002). Based on USGS data for 2006 (Figure 3), there have
been no bankfull events at this gauge. The highest flow event during 2006 was 1080 cfs
on November 22th', which is less than half of the bankfull discharge predicted by the
urban piedmont regional curve. Using the rural piedmont regional curve, bankfull
discharge is 819.7 cfs, making the high flow event on November 22nd the only bankfull
event of the year.
The 2006 qualitative evaluation of Third Fork Creek clearly indicates that at least one,
probably three storm events resulted in flows over the designed/built bankfull elevation.
Exhibit Table VIII. Verification of Bankfull Events - Third Fork Stream Restoration - EEP Project
#139
Date of Data
Collection Date of Occurrence Method Photo #
(if available)
2006 22 November 2006 Proximal USGS gauge resource NA
26 June 2006 15 June 2006 On-site high water indicators above
15 September 2006 03 September 2006 On-site high water indicators NA
Third Fork Creek Stream Restoration 2006 Monitoring Report
EEP Project # 139 Year 2 of 5
RJG&A Page 14
On-site evidence of over-bank flow (26 June 2007)
3. USUS 2006 stream
data for Ellerbe Creek near Gorman, N.C.
USES 02088849 ELLERBE CREEK NEAR GORMAN, NC
2800.6
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S
d
L
V
Vi
0
s
J
H
Jan 81 Mar 61 May 81 Jul 81 Sep 61 Now 61
2006 2886 2886 2886 2886 2886
---- Provisional Data Subject to Revision ----
Median daily statistic (9 years) - Daily nean discharge
Table IX BEHI and Sediment Export Estimates only apply to Monitoring year 5
and was, therefore, not performed during 2006 (monitoring year 2).
Third Fork Creek Stream Restoration 2006 Monitoring Report
EEP Project #139 Year 2 of 5
RJG&A Page 15
Exhibit Table X. S eam Problem Are - Third Fork Stream Restoration - EEP Project
#139
Feature/Issue Station Probable Cause Photo
A radation bar 1057 Offsite/u stream SP I
Aggradation (bar) 1080 Offsite/u stream SPI
Vane backcut/scour 1090 Insufficient/no coarse backfill SP4&5
Aggradation (pool) 1110 Offsite/upstream SP2
Aggradation (pool) 1151 Offsite/upstream SP2
Aggradation (bar) 1193 Offsite/upstream SP I
Vane backcut/scour 1419 Insufficient/no coarse backfill SP4&5
Bank undercut/slum 1517 No armor/rootwad SP3
Vane backcut/scour 1783 Insufficient/no coarse backfill SP4&5
Vane backcut/scour 2034 Insufficient/no coarse backfill, storm flow from UT SP4&5
Vane backcut/scour 2146 Insufficient/no coarse backfill SP4&5
Vane backcut/scour 2171 Insufficient/no coarse backfill SP4&5
Bank undercut/slum 2502 No armor/rootwad SP3
Bank undercut/slum 2632 No armor/rootwad SP3
Vane backcut/scour 2704 Insufficient/no coarse backfill SP4&5
Vane backcut/scour 2801 Insufficient/no coarse backfill SP4&5
A radation (bar) 3075 Double box culvert SP I
A radation bar
3152 Confluence with channelized UT below box
culverts
SP1
Aggradation (bar) 3208 Bank undercut/slum and offsite/u stream SPI
Aggradation (pool) 3216 Bank undercut/slump and offsite/upstream SP2
Aggradation (bar) 3292 Bank undercut/slump and offsite/upstream SPI
Aggradation (bar) 3322 Bank undercut/slump and offsite/upstream SPI
Aggradation (bar) 3404 Bank undercut/slump and offsite/upstream SPI
Vane backcut/scour 3410 Insufficient/no coarse backfill SP4&5
Bank undercut/slum 3427 No armor/rootwad SP3
Aggradation (bar) 3485 Bank undercut/slump and offsite/upstream SPI
Bank undercut/slum 3559 No armor/rootwad SP3
Bank undercut/slum 3664 No armor/rootwad SP3
Bank undercut/slum 3732 No armor/rootwad SP3
Bank undercut/slum 3805 No armor/rootwad SP3
Vane backcut/scour 3862 Insufficient/no coarse backfill SP4&5
Aggradation (bar) 3976 Bank undercut/slump and offsite/upstream SP I
Third Fork Creek Stream Restoration 2006 Monitoring Report
EEP Project #139 Year 2 of 5
RJG&A Page 16
xhibit Table XI. Categorical Stream Feature Visual Stability Assessment
Third Fork Creek Stream Restoration - EEP Project #139
U stream Reach 1600 Feet
Feature Initial* MY-01 MY-02 MY-03 MY-04 MY-05
A. Riffles 100% NA 92
B. Pools 100% NA 87
C. Thalwe 100% NA 69
D. Meanders 100% NA 0
E. Bed General 100% NA 100
F. Vanes/J Hooks, etc. 100% NA 93
G. Wads and Boulders NA NA NA
Downstream Reach 1525 Feet
A. Riffles 100% NA 56
B. Pools 100% NA 56
C. Thalwe 100% NA 57
D. Meanders 100% NA 67
E. Bed General 100% NA 100
F. Vanes/J Hooks, etc. 100% NA 89
G. Wads and Boulders 100% NA NA
*These percentages are assumed. Neither the As-built Monitoring Report nor the First
Year Monitoring Report contained any visual stability assessment data.
Third Fork Creek Stream Restoration 2006 Monitoring Report
EEP Project #139 Year 2 of 5
RJG&A Page 17
Exhibit Table XII. Baseline Morphology and Hydraulic Summary - Third Fork Creek Stream
Restoration- EEP Proiect #139 - Durham County, NC
Parameters Pre-existin condition
Dimension
USGS
Data Regional
Curve
Interval
U stream Reach
Downstream Reach
Flood prone Elevation ft NA NA
Bankfull Elevation ft NA NA
Flood prone Width ft 29.2-400 62-400
Bankfull Width (ft 21.8-26.8 29.5
Entrenchment Ratio 1.1-18.3 6.8
Mean Depth ft NA NA
Maximum Depth ft 4.7 5.8
Width/De th Ratio 8.3-15.9 12.2
Bankfull Areas ft 45.1-57.2 71.4
Wetted Perimeter ft NA NA
Hydraulic Radius ft NA NA
Substrate
d50 mm 0.31-0.38 0.41
d84 mm NA NA
Pattern NA NA
Channel Beltwidth ft NA NA
Radius of Curvature ft NA NA
Meander Wavelength NA NA
Meander Width ratio
Profile
Riffle length (ft) NA NA
Riffle slope (ft/ft 0.24-0.57 0.25-0.29
Pool length (ft) NA NA
Pool spacing ft NA NA
Additional Reach Parameters
Valle Length (ft) NA NA
Channel Lcn h (fl) 11890 9(_0
Sinuosity 1.03 1.01
Water Surface Slope (ft/ft) 0.25 0.20
BF slope ft/ft N ?1 NA
Rosgen Classification F5. G5, E5 C5
Habitat Index NA NA
Macrobenthos NA NA
Third Fork Creek Stream Restoration 2006 Monitoring Report
EEP Project #139 Year 2 of 5
RJG&A Page 18
Exhibit Table XIl. Baseline Morphology and Hydraulic Summary - Third Fork Creek Stream
Restoration - EEP Project #139 - Durham County, NC
Parameters Reference
Reach
Desi n
Dimension North
Prong
Creek
Upstream Reach
Downstream Reach
Flood prone Elevation ft NA NA NA
Bankfull Elevation ft NA NA NA
Flood prone Width ft NA NA NA
Bankfull Width ft 17.8 27 30
Entrenchment Ratio 33.7 2.3-14.8 6.7
Mean Depth ft 1.5 2.2 2.5
Maximum Depth ft 3.0 4.0 4.25
Width/De th Ratio 12.1 12.1 12.0
Bankf ill Areas ft 26.2 60 75
Wetted Perimeter ft NA NA NA
Hydraulic Radius ft NA NA NA
Substrate
d50 (nun) 0.20 0.31-0.38 0.41
d84 (mm) NA NA NA
Pattern
Channel Beltwidth ft 158 120 90
Radius of Curvature ft 37-40 60-75 60-80
Meander Wavelength ft 94-143 160-190 180-210
Meander Width ratio 8.9 4.4 3.0
Profile
Riffle length ft NA NA NA
Riffle slope ft/ft) 0.2-2.1 0.25-0.29 0.25
Pool length (ft) 8-30 27-40 30-45
Poolspacing (ft) 40-85.5 60-125 70-140
Additional Reach Parameters
Valley Length w) NA NA NA
Channel Length (ft) 407 2083 925
Sinuosity 1.28 1.13 1.10
Water Surface Slope (ft/ft) 0.24 0.25 _ 0
BF slope (tuft) NA NA NA
Ros en Classification C5 C5 CS
Habitat Index NA NA NA
Macrobenthos NA NA NA
Third Fork Creek Stream Restoration 2006 Monitoring Report
EEP Project #139 Year 2 of 5
RJG&A Page 19
Exhibit Table XII. Baseline Morphology and Hydraulic Summary - Third Fork Creek Stream Restoration -
EEP Project #139 - Durham County, NC
As-built*
Parameters U stream Reach Downstream Reach
Dimension min max average min max average
Flood rove Elevation ft NA NA NA NA NA NA
Bankfull Elevation fr NA NA NA NA NA NA
Flood prone Width ft NA NA NA NA NA NA
Bankf ill Width (ft) NA NA 27 NA NA 30
Entrenchment Ratio 2.3 14.8 NA NA NA 6.7
Mean Depth ft NA NA 2.2 NA NA 2.5
Maximum Depth (ft) NA NA 4.0 NA NA 4.25
Width/De th Ratio NA NA 12.1 NA NA 12.0
Bankfull Areas ft NA NA 60 NA NA 75
Wetted Perimeter ft NA NA NA NA NA NA
Hydraulic Radius (ft) NA NA NA NA NA NA
Substrate
d50 mm 0.31 0.38 NA NA NA 0.41
d84 (mm) NA NA NA NA NA NA
Pattern
Channel Beltwidth ft NA NA 120 NA NA 90
Radius of Curvature ft 60 75 NA 60 80 NA
Meander Wavelength 160 190 NA 180 210 NA
Meander Width ratio NA NA 4.4 NA NA 3.0
Profile
Riffle length ft NA NA NA NA NA NA
Riffle slope ft/ft 0.25 0.29 NA NA NA 0.25
Pool length ft 27 40 NA 30 45 NA
Pool spacing ft NA NA NA NA NA NA
Additional Reach
Parameters
Valle Length(ft) NA NA NA N,A NA NA
Channel Lcn-th 'ft} N.? N,-'' 2083 N ?\ NA
- -
-- -
Sinuosity NA NA 1.13 NA NA 1.10
Water Surface Slope
(ft/ft)
NA
NA
0.25
NA
NA
0.20
Bl PC (It NA N;\ N,\ N N,"\
Rosgen Classification NA NA C? NA NA C-5
Habitat Index NA NA NA NA NA
Macrobenthos NA NA NA NA NA
*No as-built numbers were provided. The Third Fork mitigation plan (December 2005)
and the First Year Monitoring Report (December 2005) both provide Design numbers
only, therefore the design numbers have been provided in the as-built columns, but are
redundant of those figures appearing earlier in the table.
Third Fork Creek Stream Restoration 2006 Monitoring Report
EEP Project #139 Year 2 of 5
RJG&A Page 20
F,xhihit Tahle Xiii_ Marnhnlnuv and Hvdraulic Monitorinu Snmmarv - Third Fnrk Creek StrPnm RPctnratinn _ Ti Ti P Pr-of IWAO
XS 1 XS 2 XS 3 XS 4
Dimension As-
built Mon
01
Mon 02 As-
built
Mon 01
Mon 02 As-
built
Mon 01
Mon 02 As-
built Mon
01
Mon 02
Flood rove Elevation ft 301.46 301.49 301.74 301.88 302.21 302.65 295.37 295.75 295.88 297.07 297.50 297.05
Bankfull Elevation (ft) 297.55 297.54 297.55 297.07 297.10 297.20 292.09 292.27 292.40 292.56 292.53 292.49
Flood rove Width (ft) 240.00 240.00 240.00 240.00 240.00 240.00 240.00 240.00 240.00 240.00 240.00 240.00
Bankfull Width ft 20.40 27.11 28.63 26.43 26.39 27.62 17.50 29.00 25.97 17.50 23.29 20.47
Entrenchment Ratio 11.76 8.85 8.38 9.08 NA 8.69 13.71 8.28 9.24 13.71 NA 11.72
Mean Depth (ft) 3.03 2.26 2.18 2.65 2.76 2.78 3.12 1.84 1.84 3.51 2.59 2.80
Maximum Depth ft 3.91 3.95 4.19 4.81 5.11 5.45 3.28 3.48 3.84 4.51 4.97 4.56
Width/De th Ratio 6.70 12.00 13.12 9.97 NA 9.94 5.61 15.70 14.51 4.98 NA 7.31
Bankfull Areas ft 61.87 61.37 62.47 70.07 72.88 76.71 54.61 53.46 47.67 61.50 60.40 57.34
Wetted Perimeter ft NA NA 30.91 NA NA 31.70 NA NA 28.31 NA NA 23.99
Hydraulic Radius ft NA NA 2.02 NA NA 2.42 NA NA 1.68 NA NA 2.39
Substrate
d50 mm 0.06 0.04 0.06 0.09 0.49 6.27 1.00 0.85
d84 (mm) 0.60 0.06 0.10 0.78 1.50 16.6 2.00 11.3
Upstream Reach Downstream Reach
Pattern As-
built Mon
01
Mon 02 As-
built
Mon 01
Mon 02
Channel Beltwidth ft NA NA 33.88 NA NA 35.77
Radius of Curvature (ft) NA NA 69.42 NA NA 57.96
Meander Wavelength NA NA 177.65 NA NA 162.56
Meander Width ratio NA NA 1.20 NA NA 1.54
Profile
Riffle length ft NA NA 51.43 NA NA 14.24
Riffle slope ft/ft)
NA 0.001-
0.002
0.002
NA 0.001-
0.011
0.02
Pool length (ft) NA 28.60 NA NA 101.45
Poolspacing (ft) NA 45-115 35.95 NA 14-82 23.28
rauu111011al neacn rararnerers
Valley Length (fl) NA NA 3 t U NA NA 308
Channel Length (ft) NA NA 3j0 NA NA 350
Sinuosity NA NA I I N\ %A 1.14
Water Surface Slope (ff/ft) NA NA ?ni? N A N \ 0.0009
BF slope (ft/ft) NA NA 0.0003 NA NA 0.013
Rosgcn CIassi?lca[ion NA NA CS NA NA C51)
Habitat Index NA NA NA NA NA NA
Macrobenthos NA NA
Third Fork Creek Stream Restoration 2006 Monitoring Report
EEP Project #139 Year 2 of 5
RJG&A Page 21
C. Wetland Assessment
No wetland restoration was included in this project.
Third Fork Creek Stream Restoration
EEP Project #139
RJG&A
2006 Monitoring Report
Year 2 of 5
Page 22
Appendix A
(Click here)