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hird Fork Creek Stream Restoration - NCEEP Project #139
Durham, North Carolina
Second Annual Monitoring Report December 2006
Designed by:
KCI Associates of North Carolina, P.A.
Landmark Center II, Suite 220
4601 Six Forks Road
Raleigh, North Carolina 27609
Submitted to:
North Carolina Department of Environment and
Natural Resources
Ecosystem Enhancement Program
1652 Mail Service Center
Raleigh, NC 27699-1652
PMOG4t~
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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
I. Executive Summary""",......"., ,.,.""....... ,....." ..."..,.."..,.........'.." ,."."",..........."".........,. 3
II. Proj ect 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 ,.......................,..........................,............, ......,.. ..........." 1 0
3. Stem Counts ".."" ",.".".......,...,.....".....,.......,..,.,.....,."."... ,.......,..".,....",.,.........., 1 0
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
EEP Project #139
RJG&A
2006 Monitoring Report
Year 2 of5
Page 1
APPENDICES
Appendix A Vegetation Raw Data
A-I 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.l 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
EEP Project #139
RJG&A
2006 Monitoring Report
Year 2 of5
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
Surveyl4-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 of2002.
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 15/501 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
EEPProject#139 Year2of5
RJG&A Page 3
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
~m. The buffers' outer twenty feet was planteq in native grasses and i~ managed
(mowed). 0\
..,...-~ cP
vi'-
Third Fork Creek Stream Restoration
EEP Project #139
RJG&A
2006 Monitoring Report
Year 2 of5
Page 4
Third Fork Creek Stream Restoration
EEP Project #139
RJG&A
2006 Monitoring Report
Year 2 of 5
Page 5
Exhibit Table I. Mitigation Structure and Objectives - Third Fork Creek Stream Restoration - EEP
Project #139 - Durham, NC
Reach ill Mitigation
Type
Approach
Linear
Feet
Stationing Mitigation
Credits (ratio)
Upstream Restoration Priority 2
10+00-
26+00
o
o
0'1
C'l~
,.-,.
........
........
'--'
Downstream Restoration Priority 2
25+00 -
40+25
C'l
0'1
t'-~
C'f')
C. History and Background
As-built
March 2005
Year 1 Monitoring
Geomo
Year 2 Monitoring
Comment
.s
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Third Fork Creek Stream Restoration
EEP Project #139
RJG&A
2006 Monitoring Report
Year 2 of 5
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. Proiect Background - Third Fork Creek Stream - EEP Pro,ject #139
County Durham
Drainage Area 1,126.4 acres (1.76 square miles)
Drainage Impervious Cover Estimate (%) 44%
Stream Order Second Order
Phvsiographic Region Piedmont
Ecoregion Triassic Basins
Rosgen 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 C
Reference
Anv portion of the project segment 303d listed? Yes
Any portion of the project segment upstream of Yes
a 303d listed segment?
Reasons for 303d Listing or Stressor Turbidity, low dissolved oxygen, fecal coliform
bacteria
% ofProiect Easement Fenced 0%
Third Fork Creek Stream Restoration
EEP Project #139
RJG&A
2006 Monitoring Report
Year 2 of5
Page 7
Figure 2. Monitoring Plan View
Third Fork Creek Stream Restoration
EEP Project #139
RJG&A
2006 Monitoring Report
Year 2 of 5
Page 8
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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 (Le. 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. ~el!etation Problem Ams - Third Fork Creek Stream - EEP
Proiect #139 - Durham, NC
Feature/Issue Station/Ranl!e Probable Cause Photo #
Exotic Invasive Vines 12+75 - 14+00 Colonization of floodplain by VP2&3
waterborne seeds
Exotic Invasive 12+75 - 14+00 Colonization by air and water VP4&5
Woody Stems borne seeds
Exotic Invasive vines 16+75 - 19+75 Colonization of floodplain by VP2&3
waterborne seeds
Exotic Invasive vines 20+75 - 22+40 Colonization of floodplain by VP2&3
waterborne seeds
Exotic Invasive vines 24+60 - 26+25 Colonization of floodplain by VP2&3
waterborne seeds
Third Fork Creek Stream Restoration
EEP Project #139
RJG&A
2006 Monitoring Report
Year 2 of 5
Page 9
Exhibit Table VI. Vegetation Problem Areas - Third Fork Creek Stream - EEP
Pro,ject #139 - Durham, NC
Disturbed area 29+90 - 30+80 Diseased tree removal by City of VP1
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 porcelainbeny (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 entire 1 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)),
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, Levell (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 comers 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 (em) were
recorded,
Third Fork Creek Stream Restoration
EEP Project #139
RJG&A
2006 Monitoring Report
Year 2 of5
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
EEP Project #139
RJG&A
2006 Monitoring Report
Year 2 of 5
Page 11
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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-Iocated 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 0 I 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
\riJ. eqll,ili rate themselves over time. The only other significant problem area (i.e, remedial
, \ .. ~V--~tion should be considered) is a backcutj-hook that has had its upstream-most header
. ~ V- / rock undercut (station 27+04), The rock has been completely dislodged and fallen back
\)J Y (upstream) into the scoured channel. The remainingj-hook/cross vane problem areas are
~ CY~\ relatively minor and should continue to be observed, to determine if remedial action
~ should occur.
X\Q~>
~ A wetted perimeter bed material analysis was performed at each cross section during
October 2006. The difference between the second annual monitoring substrate analysis
. . . J:!^ and the first year's indicates that the upstream-most channel bed has become finer (KS I),
.,.. -... ~ (1 while the downstream-most bed (xs2-4) have become coarser. The most significant
~/' change was observed at cross section 3.
~ ^>P
~'t~
Third Fork Creek Stream Restoration
EEP Project #139
RJG&A
2006 Monitoring Report
Year 2 of5
Page 13
On-site evidence of over-bank flow (26 June 2007)
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 of21.9 square miles would reach a bankfull discharge at 2,144.5 cubic feet per
second (cfs) (Doll et aI., 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 2ih" 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 designedlbuilt bankfull elevation.
Exhibit Table VIII. Verification of Bankfull Events - Third Fork Stream Restoration - EEP Project
#139
Date of Data Date of Occurrence Method Photo #
Collection (if available)
2006 22 November 2006 Proximal USGS Qam!e resource NA
26 June 2006 15 June 2006 On-site hiQh water indicators above
15 September 2006 03 September 2006 On-site hiQh water indicators NA
Third Fork Creek Stream Restoration
EEP Project #139
RJG&A
2006 Monitoring Report
Year 2 of5
Page 14
iI USGS
"'Cl 2999.9
c
o
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USGS 02086849 ELLERBE CREEK NIEAR GORMAN, NC
10:0
Jan 91
2996
Jul 91
2996
Nov 81
2996
l1ar 81
2996
l1ay 81
2996
Sep 81
2996
---- Provisional Data Subject to Revision ----
--- l1edian 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
EEP Project #139
RJG&A
2006 Monitoring Report
Year 2 of5
Page 15
Exhibit Table X. ~roble~ - Tbird Fork Stream Restoration - EEP Project
#139
Feature/Issue Station Probable Cause Photo
Aggradation (bar) 1057 Off site/upstream SP1
Aggradation (bar) 1080 Offsite/upstream SP1
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 Off site/upstream SP1
Vane backcut/scour 1419 Insufficient/no coarse backfill SP4&5
Bank undercut/slump 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/slump 2502 No armor/rootwad SP3
Bank undercut/slump 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
Aggradation (bar) 3075 Double box culvert SP1
Confluence with channelized UT below box
Aggradation (bar) 3152 culverts SP1
Aggradation (bar) 3208 Bank undercut/slump and offsite/upstream SP1
Aggradation (pool) 3216 Bank undercut/slump and offsite/upstream SP2
Aggradation (bar) 3292 Bank undercut/slump and offsite/upstream SP1
Aggradation (bar) 3322 Bank undercut/slump and offsite/upstream SP1
Aggradation (bar) 3404 Bank undercut/slump and off site/upstream SP1
Vane backcut/scour 3410 Insufficient/no coarse backfill SP4&5
Bank undercut/slump 3427 No armor/rootwad SP3
Aggradation (bar) 3485 Bank undercut/slump and offsite/upstream SP1
Bank undercut/slump 3559 No armor/rootwad SP3
Bank undercut/slump 3664 No armor/rootwad SP3
Bank undercut/slump 3732 No armor/rootwad SP3
Bank undercut/slump 3805 No armor/rootwad SP3
Vane backcut/scour 3862 Insufficient/no coarse backfill SP4&5
Aggradation (bar) 3976 Bank undercut/slump and offsite/upstream SPl
Third Fork Creek Stream Restoration
EEP Project #139
RJG&A
2006 Monitoring Report
Year 2 of 5
Page 16
~Xhibit Table XI. Categorical Stream Feature Visual Stability Assessment
Third Fork Creek Stream Restoration - EEP Project #139
Upstream 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, Thalweg 100% NA (69)
D, Meanders 100% NA 90
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 136,
B. Pools 100% NA I 56 )
C. Thalweg 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
EEP Project #139
RJG&A
2006 Monitoring Report
Year 2 of 5
Page 17
Exhibit Table XII. Baseline Morphology and Hydraulic Summary - Third Fork Creek Stream
Restoration- EEP Pro' ect #139 - Durham County, NC
Parameters Pre-existin condition
Regional
Curve
Interval
Pattern
Channel Beltwidth ft
Radius of Curvature ft
Meander Wavelen th
Meander Width ratio
Additional Reach Parameters
USGS
Data
Downstream Reach
U stream Reach
NA
NA
29,2-400
21.8-26,8
1.1-18.3
NA
4.7
8.3-15,9
45,1-57,2
NA
NA
NA
NA
62-400
29.5
6,8
NA
5,8
12,2
71.4
NA
NA
0.31-0.38
NA
0.41
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
0.24-0.57
NA
NA
NA
0,25-0,29
NA
NA
Third Fork Creek Stream Restoration
EEP Project #139
RJG&A
2006 Monitoring Report
Year 2 of 5
Page 18
Exhibit Table XII. Baseline Morphology and Hydraulic Summary - Third Fork Creek Stream
Restoration - EEP Project #139 - Durham County, NC
Reference
Parameters Reach Desi n
North
Prong
Creek U stream Reach Downstream Reach
NA NA NA
NA NA NA
NA NA NA
17.8 27 30
33.7 2,3-14,8 6,7
1.5 2,2 2.5
3,0 4,0 4.25
12.1 12,1 12,0
26.2 60 75
NA NA NA
NA NA NA
0,20 0.31-0.38 0.41
NA NA NA
Pattern
Channel Beltwidth ft 158 120 90
Radius of Curvature ft 37-40 60-75 60-80
Meander Wavelen th ft 94-143 160-190 180-210
Meander Width ratio 8,9 4.4 3,0
NA NA NA
0,2-2.1 0,25-0,29 0,25
8-30 27-40 30-45
40-85,5 60-125 70-140
Additional Reach Parameters
Third Fork Creek Stream Restoration
EEP Project #139
RJG&A
2006 Monitoring Report
Year 2 of5
Page 19
Exhibit Table XII. Baseline Morphology and Hydraulic Summary - Third Fork Creek Stream Restoration -
EEP Project #139 - Durham County, NC
Parameters Upstream Reach Downstream Reach
Dimension mm max average min max average
Floodprone Elevation (ft) NA NA NA NA NA NA
Bankfull Elevation (ft) NA NA NA NA NA NA
Floodprone Width (ft) NA NA NA NA NA NA
Bankfull 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 Deoth (ft) NA NA 4,0 NA NA 4.25
Width/Depth Ratio NA NA 12,1 NA NA 12.0
Bankfull Area (sq 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 (ftlft) 0,25 0,29 NA NA NA 0.25
Pool length (ft) 27 40 NA 30 45 NA
Pool soacing (ft) NA NA NA NA NA NA
Additional Reach
Parameters
Sinuosity NA NA 1.13 NA NA 1.l0
Water Surface Slope
Habitat Index NA NA NA NA NA
Macrobenthos NA NA NA NA NA
As-built*
*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 ofthose figures appearing earlier in the table,
Third Fork Creek Stream Restoration
EEP Project #139
RJG&A
2006 Monitoring Report
Year 2 of 5
Page 20
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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