HomeMy WebLinkAbout20030158 Ver 1_Complete File_20030213B-3401
BRIDGE PROJECT
SCOPING SHEET
State Project No. 8.2472501 Right of Way 2-01
Federal Project No. BRZ-1921(3) Construction Let 2-02
Purpose of Project: REPLACE OBSOLETE BRIDGE
Description of Project: Replace Bridge No. 60 on SR 1921 over Quaker Creek in
Alamance County, B-3401.
Bridge No. 60 LENGTH 46 METERS; WIDTH 7.6 METERS
151 FEET 25 FEET
TIP CONSTRUCTION COST ...................................... $ 500,000
TIP RIGHT OF WAY COST ...................................... + $ 50,000
TIP TOTAL COST .................................... $ 550,000
CLASSIFICATION: Rural Local Route
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North Carolina
. Department of Transportation
Division of Highways
Planning & Environmental Branch
Alamance County
Replace Bridge No. 60 on SR 1921
Over Quaker Creek
B-3401
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ID AND 1969 MAGNETIC NORTH
DECLINATION AT CENTER OF SHEET
5156 Ill SE 17 30
SCALE 1:24000
1 7 0 1 MILE
1000 0 1000 2000 3000 4000 5000 6000 7000 FEET
1 5 D 1 KILOMETER
CONTOUR INTERVAL 10 FEET
DATUM IS MEAN SEA LEVEL
THIS MAP COMPLIES WITH NATIONAL MAP ACCURACY STANDARDS
FOR SALE BY U. S. GEOLOGICAL SURVEY, WASHINGTON, D. C. 20242
A FOLDER DESCRIBING TOPOGRAPHIC MAPS AND SYMBOLS IS AVAILABLE ON REQUEST
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STATE OF NORTH CAROLINA
DEPARTMENT OF TRANSPORTATION
MICHAEL F. EASLEY
GOVERNOR
February 14, 2003
US Army Corps of Engineers
Regulatory Field Office
6508 Falls of Neuse Road, Suite 120
Raleigh, NC 27615
ATTENTION: Mr. John Thomas
NCDOT Coordinator
0301 58
LYNDO TIPPETT
SECRETARY
,11WE
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GROUP
I,1 !1,,* SECTION_
Subject: Nationwide 23 Permit Application for the Replacement of Bridge No. 60 over
Quaker Creek on SR 1921, Alamance County. Federal Aid Project No.
BRSTP-1921(3), State Project No. 8.2472501, TIP Project No. B-3401.
Dear Sir:
Please find enclosed three copies of the project planning report for the above
referenced project. The document states that Bridge No. 60 will be replaced with a new
240-foot [73 meters (m)] long bridge on new alignment approximately 50 feet (ft) (15 m)
north of the existing structure. The cross section of the new bridge will include two 12-
foot (3.5 m) wide lanes with 3-foot (1 m) wide offsets (shoulders). Construction of the
bridge will be with A-frame pile bents, therefore top-down construction will be
implemented. Traffic will be maintained on the existing bridge during construction. An
existing roadside ditch is located in the northeast quadrant of the project. Existing fill
from the roadbed on the east side of the bridge will be removed and the existing roadside
ditch will be relocated there.
There will be 400 ft (122 m) of new approach work to the east and 500 ft (152 m)
of new approach work to the west. The pavement width on the approaches will be 24 ft
(7.2 m) including two 12-foot (3.6 m) lanes. Additionally, there will be 8-foot (2.4 m)
grass shoulders.
There are no wetland impacts are associated with this project. The only surface
water impacted by this project is Quaker Creek. Quaker Creek at this point is part of
Quaker Creek Reservoir (see attached drawing sheets 1-4). Quaker Creek is classified by
the Division of Water Quality as WS-II NSW in the Categorical Exclusion (CE)
MAILING ADDRESS: TELEPHONE: 919-733-3141 LOCATION:
NC DEPARTMENT OF TRANSPORTATION FAX: 919-733-9794 TRANSPORTATION BUILDING
PROJECT DEVELOPMENTAND ENVIRONMENTAL ANALYSIS 1 SOUTH WILMINGTON STREET
1548 MAIL SERVICE CENTER WEBSITE: WWW.NCDOT.ORG RALEIGH NC
RALEIGH NC 27699-1548
document. Since then the classification has changed to WS-II HQW NSW CA. The
change now designates this area of the stream as High Quality Waters (HQW).
NCDOT's High Quality Waters Standards will be enforced throughout project
construction.
Quaker Creek will be impacted through 0.09 acres (ac) of fill. After the removal
of the existing bridge, the current fill will be excavated to provide for storage of surface
waters in the Quaker Creek Reservoir. This will result in an increase in surface water of
0.16 ac for this project (sheets 4, 5 and 6).
This project is classified as Case 2 which allows no work in the water during
moratorium periods associated with fish migration, spawning and larval recruitment into
nursery areas. An in-water work moratorium from April 1 to June 15 will be required for
this project due to the quality largemouth bass population that the lake supports. Also, all
measures will be taken as outlined in the Best Management Practices for Protection of
Surface Waters.
Demolition: Bridge No. 60 is composed entirely of timber and steel. The bridge
railings and substructure will be removed without dropping components into Waters of
the United States. All guidelines for bridge demolition and removal will be followed in
addition to Best Management Practices for the Protection of Surface Waters.
This project is being processed by the Federal Highway Administration as a
"Categorical Exclusion" in accordance with 23 CFR 771.115(b). Therefore, we do not
anticipate requesting an individual permit but propose to proceed under a Nationwide 23
in accordance with the Federal Register of December 13, 1996, Part VII, Volume 61,
Number 241. We anticipate a 401 General Certification number 3361 will apply to this
project. In accordance with 15A NCAC 2H .0501(a) we are providing two copies of this
application to the North Carolina Department of Environment and Natural Resources,
Division of Water Quality, for their records.
If you have any questions or need additional information, please contact Rachelle
Beauregard at (919) 715-1383.
Sincerely,
V ' I ' pGregory J. Thorpe, Ph.D.
Environmental Management Director, PDEA
w/ attachment:
Mr. John Dorney, NC Division of Water Quality (2 copies)
Mr. Gary Jordan, USFWS
Mr. Travis Wilson, NCWRC
Mr. Greg Perfetti, P.E., Structure Design
w/o attachment
Mr. David Franklin, USACE, Wilmington
Mr. Jay Bennett, P.E., Roadway Design
Mr. Omar Sultan, Programming and TIP
Ms. Deborah Barbour, PE, Highway Design
Mr. David Chang, P.E., Hydraulics
Ms. Mark Staley, Roadside Environmental
Mr. J.M. Mills, P.E., Division 7 Engineer
Mr. John Williams, Project Development and Environmental Analysis Branch
Mr. Jerry Parker, Division 7 Environmental Officer
VICINITY MAP
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N. C. DEPT. OF TRANSPORTATION
DIVISION OF HIGHWAYS
ALAMANCE COUNTY
PROJECT: 8.2472501 B-3401
SHEET 1 OF 7 9/ 17/ 02
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LEGEND
---WLB WETLAND BOUNDARY
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LIVE STAKES
- WETLAND
® DENOTES FILL IN
WETLAND
® DENOTES FILL
SURFACE WATER
R
® DENOTES FILL
SURFACE WATER
R
(POND)
T T DENOTES TEMPORARY
FILL IN WETLAND
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FILL IN SURFACE WATER
• DENOTES MECHANIZED
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TB
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---WE--- EDGE OF WATER
- C - PROP. LIMIT OF CUT
F - PROP. LIMIT OF FILL
-?- PROP. RIGHT OF WAY
- - NG- - NATURAL GROUND
PROPERTY LINE
-TOE- TEMP. DRAINAGE
EASEMENT
-PDE- PERMANENT DRAINAGE
EASEMENT
-EAB- EXIST. ENDANGERED
ANIMAL BOUNDARY
-EPB- EXIST. ENDANGERED
PLANT BOUNDARY
--- 0------- WATER SURFACE
N. C. DEPT. OF TRANSPORTATION
DIVISION OF HIGHWAYS
ALAMANCE COUNTY
BOULDER
COIR FIBER ROLLS
O ADJACENT PROPERTY OWNER
OR PARCEL NUMBER
PROPOSED BRIDGE
PROPOSED BOX CULVERT
PROPOSED PIPE CULVERT
(DASHED LINES DENOTE
EXISTNG STRUCTURES)
,J SINGLE TREE
WOODS LINE
¦ DRAINAGE INLET
ROOTWAD
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RIP RAP
RIP RAP ENERGY
DISSIPATOR BASIN
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BUFFER ZONE BUFFER ZONE
PROJECT: 8.2472501 B-3401
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PROPERTY OWNER
NAME AND ADDRESS
OWNER'S NAME ADDRESS
P.O. Drawer 357
201 South Main Street
6 CITY OF GRAHAM
Graham, NC 27253
N. C. DEPT. OF TRANSPORTATION
DIVISION OF HIGHWAYS
ALAMANCE COUNTY
PROJECT: 8.2472501 B-3401
SHEET 6 OF 7 9/17/02
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Alamance County
Bridge No. 60 on SR 1921
Over Quaker Creek
Federal Project BRZ-1921(3)
State Project 8.2472501
TIP No. B-3401
CATEGORICAL EXCLUSION
U. S. DEPARTMENT OF TRANSPORTATION
FEDERAL HIGHWAY ADMINISTRATION
AND
N. C. DEPARTMENT OF TRANSPORTATION
DIVISION OF HIGHWAYS
APPROVED:
g- i F-00
?-fc„ v
Date William D. Gilmore, P. E., Manager
Project Development and Environmental Analysis Branch
'8-z3-oo koc??`7
Date Nicholas Graf, P. E.
Division Administrator, FHWA
I I
Alamance County
Bridge No. 60 on SR 1921
Over Quaker Creek
Federal Project BRZ-1921(3)
State Project 8.2472501
TIP No. B-3401
CATEGORICAL EXCLUSION
AUGUST 2000
-n - 00
Date
Documentation Prepared in
Project Development and Environmental Analysis Branch By:
Jofin L. Williams, P. E.
Project Planning Engineer
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Date Wayne lliott
Bridge Project Planning Engineer, Unit Head
Date Lubin V. Prevatt, P. E., Assistant Manager
Project Development and Environmental Analysis Branch
I / 0 1
PROJECT COMMITMENTS:
B-3401, Alamance County
Bridge No. 60 on SR 1921
Over Quaker Creek
Federal Project BRZ-1921(3)
State Project 8.2472501
Resident Engineer
Bridge Demolition: Best Management Practices for Bridge Demolition &
Removal will be implemented.
Moratorium: A moratorium will be implemented from April l to June 15 of any
construction period to protect largemouth bass spawning periods.
Sensitive Watersheds: Best Management Practices for Protection of Sensitive
Watersheds will be implemented during construction
Roadside Environmental Unit
Sensitive Watersheds: Best Management Practices for Protection of Sensitive
Watersheds will be implemented during construction
Structure Design
Bridge Demolition: Best Management Practices for Bridge Demolition &
Removal will be implemented.
Hydraulics
Hazardous Spill Catch Basin: NCDOT Hydraulics Unit has reviewed this
project to determine the necessity of a hazardous spill catch basin. A close review has
determined that the project lies just outside the waters listed as WSII and therefore does
not require the study of a hazardous spill catch basin.
Sensitive Watersheds: Best Management Practices for Protection of Sensitive
Watersheds will be implemented during construction
Categorical Exclusion
Green Sheet
August 17, 2000
Page 1 of 1
Alamance County
Bridge No. 60 on SR 1921
Over Quaker Creek
Federal Project BRZ-1921(3)
State Project 8.2472501
TIP No. B-3401
Bridge No. 60 is located in Alamance County over Quaker Creek. It is programmed in
the Draft 2002-2008 Transportation Improvement Program (TIP) as a bridge replacement
project due to deteriorating structural integrity and a deficient cross section. This project
is part of the Federal Highway Bridge Replacement and Rehabilitation Program
(HBRRP) and has been classified as a "Categorical Exclusion". No substantial
environmental impacts are expected.
1. SUMMARY OF RECOMMENDATIONS
Bridge No. 60 will be replaced as recommended in Alternate 2 with a new 240- foot (73-
meter) long bridge on new alignment approximately 50 feet (15 meters) north of the
existing structure (see Figure 2). The cross section of the new bridge will include two
12-foot (3.6-meter) wide lanes with 3-foot (1-meter) wide offsets (shoulders). Traffic
will be maintained on the existing bridge during construction
There will be 400 feet (122 meters) of new approach work to the east and 500 feet (152
meters) of new approach work to the west. The pavement width on the approaches will
be 24 feet (7.2 meters) including two 12-foot (3.6-meter) lanes. Additionally there will
be 8-foot (2.4-meter) grass shoulders. Based on preliminary design, the design speed
should be approximately 55 mph (90 kph).
The estimated cost of the project is $1,271,000 including $1,230,000 in construction costs
and $41,000 in right of way costs. The estimated cost shown in the Draft 2002-2008 TIP
is $650,000.
II. ANTICIPATED DESIGN EXCEPTIONS
NCDOT does not anticipate any design exceptions.
III. EXISTING CONDITIONS
SR 1921 is classified as an Urban Local Route in the Statewide Functional Classification
System. It is located northeast of Burlington. Currently the traffic volume is 1800
vehicles per day (VPD) and projected at 3800 VPD for the year 2025. There is a posted
speed limit of 55 mph in the vicinity of the bridge. The area is largely residential.
The existing bridge was completed in 1960. It is composed of a four-span timber and
steel structure. The deck is 151 feet long and 24 feet wide. There is vertical clearance of
approximately 10 feet between the floorbeams of the bridge deck and streambed. The
bridge carries two lanes of traffic.
According to Bridge Maintenance Unit records, the sufficiency rating of the bridge is
20.4 out of a possible 100. Presently the bridge is posted with weight restrictions of 17
tons for single vehicles and 22 tons for truck-tractor semi-trailers.
Both vertical and horizontal alignment are fair in the project vicinity. The pavement
width on the approaches to the existing bridge is 20 feet. Shoulders on the approaches of
the bridge are approximately 4 feet wide.
In a recent three year period one accident was reported. The accident was attributed to
driver error and there is no other indication of an accident history associated with the
bridge.
There are 14 daily school bus crossings over the studied bridge. According to the
Transportation Director for Alamance County, closing the road would create a significant
burden on their transportation system.
Bell South Telephone has an underground cable along the north side of SR 1921. Time-
Warner Cable Television has underground cables along the north side of SR 1921 west of the
existing bridge. The cables are aerial across Quaker Creek and remain aerial east of the
existing bridge.
IV. PROPOSED ALTERNATIVES
There are two "build" options considered in this document as follows:
Alternate 1) Replace Bridge No. 60 on the existing location. Traffic would be
maintained with a temporary onsite detour to the north during
construction. Because of the existing causeway, this alternate would
require a 160-foot (49-meter) long bridge. The design speed would be
approximately 55 mph (90 kph).
Alternate 2) (Recommended) Replace Bridge No. 60 on new location to the east.
Traffic would be maintained on the existing bridge during construction.
Because there is no existing causeway along this alignment, Alternate 2
would require a 240-foot (73-meter) long bridge. The design speed will be
approximately 55 mph (90 kph).
An offsite detour was considered but discarded due to disruption to Emergency Medical
& Rescue Services, disruption of School Bus services, and high volumes of traffic.
"Do-nothing" is not practical; requiring the eventual closing of the road as the existing
bridge completely deteriorates. Rehabilitation of the existing deteriorating bridge is
neither practical nor economical.
2
V. ESTIMATED COST (Table 1
COMPONENT
ALTERNATE 1 Recommended
ALTERNATE 2
New Bridge
Temporary Detour Structure
Bridge Removal
Roadway & Approaches 360,000
144,000
23,000
469,000 540,000
N/A
23,000
273,000
Mobilization & Miscellaneous 354,000 244,000
Engineering & Contingencies 200,000 150,000
Total Construction $ 1,550,000 $1,230,000
Right of Way $ 31,000 41,000
Total Cost $ 1,58500 1,271,000
VI. RECOMMENDED IMPROVEMENTS
Bridge No. 60 will be replaced as recommended in Alternate 2 with a new 240-foot (73-
meter) long bridge on new alignment approximately 50 feet (15 meters) north of the
existing structure (see Figure 2). The cross section of the new bridge will include two
12-foot (3.6-meter) wide lanes with 3-foot (1-meter) wide offsets (shoulders). Traffic
will be maintained on the existing bridge during construction
There will be 400 feet (122 meters) of new approach work to the east and 500 feet (152
meters) of new approach work to the west. The pavement width on the approaches will
be 24 feet (7.2 meters) including two 12-foot (3.6-meter) lanes. Additionally there will
be 8-foot (2.4-meter) grass shoulders. Based on preliminary design, the design speed
should be approximately 55 mph (90 kph).
Both Alternates 1 and 2 were designed to prevent disruption to traffic. The environmental
impacts are only marginally higher for Alternate 2. There are two outstanding
environmental issues at this location. The bridge is at the confluence of Quaker Creek
Reservoir. These waters are classified as a WSII and are a water supply to the City of
Burlington. This location is also of significant concern to the Wildlife Resource
Commission due to excellent aquatic life resources. So long as NCDOT adheres to the
Project Commitments listed in the attached Greensheet, both alternates would equally
address the environmental concerns. Taking these factors into account and considering
the total cost of each alternate, Alternate 2 is recommended because of lower overall
costs. The Division concurs in the recommendation.
VII. ENVIRONMENTAL EFFECTS
A. GENERAL
This project is expected to have an overall positive impact. Replacement of an
inadequate bridge will result in safer traffic operations.
This project is considered to be a "Categorical Exclusion" due to its limited scope and
insignificant environmental consequences.
This bridge replacement will not have a substantial adverse effect on the quality of the
human or natural environment by implementing the environmental commitments of this
document in addition to use of current NCDOT standards and specifications.
Currently SR 1921 is not a designated Bicycle Route and there are no known bicycle
concerns for this facility. The bridge cross section is being designed accordingly.
The project is not in conflict with any plan, existing land use, or zoning regulation. No
change in land use is expected to result from construction of this project.
There are no hazardous waste impacts.
No adverse effect on families or communities is anticipated. Right-of-way acquisition
will be limited.
No adverse effect on public facilities or services is expected. The project is not expected
to adversely affect social, economic, or religious opportunities in the area.
There are no publicly owned parks, recreational facilities, or wildlife and waterfowl
refuges of national, state, or local significance in the vicinity of the project. This project
will not impact any resource protected by Section 4(f) of the DOT act.
The proposed bridge replacement project will not raise the existing flood levels or have
any significant adverse effect on the existing floodplain.
Utility impacts are considered to be low for the proposed project.
B. AIR AND NOISE
This project is an air quality "neutral" project, so it is not required to be included in the
regional emissions analysis and a project level CO analysis is not required.
The project will not increase traffic volumes. Therefore, it will not have an impact on
noise levels. Temporary noise increases may occur during construction.
C. LAND USE & FARMLAND EFFECTS
This project will have no impact on soils considered to be prime or important farmland.
D. HISTORICAL EFFECTS & ARCHAEOLOGICAL EFFECTS
On December 28, 1998, the State Historic Preservation Office (SHPO) reviewed the
subject project. Subsequently, the SHPO determined that this project is not likely to
affect any resources of architectural or archaeological significance (see attachments).
E. NATURAL RESOURCES
PHYSICAL RESOURCES
Soil and water resources that occur in the study area are discussed below. Soils and
availability of water directly influence composition and distribution of flora and fauna in
any biotic community.
The project study area lies within the Piedmont Physiographic Province. The topography
in this section of Alamance County is characterized by gently rolling hills that range from
nearly level to steep. Topography in the project area is relatively flat since it is located
within the flood plain of the Quaker Creek. Project elevation is approximately 164.6
meters (540.0 feet) above mean sea level (msl).
Soils
Five soil phases occur within project study area: Enon fine sandy loam eroded sloping
phase, Lloyd loam eroded sloping phase, Lloyd loam moderately steep phase, mixed
alluvial land poorly drained, and Worsham sandy loam.
Enon fine sand loam, eroded sloping phase, with 6 to 10 percent slopes, is a well-
drained soil on ridge tops and side slopes in the Piedmont. Permeability is slow and
runoff is medium to rapid. Main limitations of this soil include slope, surface runoff, and
erosion.
Lloyd loam eroded sloping hase, with 6 to 10 percent slopes, is a well-drained soil that
occurs on slopes. Permeability is moderate and medium to rapid surface runoff. Erosion
is a limitation of this soil.
Lloyd loam moderatel% steep hase, with 15 to 25 percent slopes, is a well-drained soil
that occurs on slopes. Permeability is moderate and medium to rapid surface runoff.
Erosion is a limitation of this soil.
Mixed alluvial land oorl drained occurs on first bottoms that border meandering
streams with shallow banks. it is somewhat poorly drained to poorly drained. Wetness is
the main limitation.
Worsham sand loam, with 2 to 6 percent slopes, occurs on foot slopes and saddles in
ow, wet depression-s. This soil is poorly drained, runoff is slow and internal drainage is
very slow. Permeability is slow to very slow. Wetness is the main limitation.
Water Resources
This section contains information concerning those water resources likely to be impacted
by the project. Water resource information encompasses physical aspects of the resource,
its relationship to major water systems, Best Usage Standards and water quality of the
resources. Probable impacts to surface water resources and minimization methods are
also discussed.
Waters Impacted and Characteristics
Quaker Creek will be the only surface water resource directly impacted by the proposed
project (Figure 2). Quaker Creek is located in sub-basin 03-06-02 of the Cape Fear River
Basin. The average baseflow width is approximately 39.6 meters (130.0 feet). The
average depth is approximately 1.2 meters (4.0 feet). Quaker Creek's substrate is
primarily silty sediment.
Best Usage Classification
Streams have been assigned a best usage classification by the DWQ. The classification
of Quaker Creek (DEM Index No. 16-18-4(1)) is WS-II NSW. The WS-II classification
identifies waters used as sources of water supply for drinking, culinary, or food
processing purposes for those users desiring maximum protection for their water supply
where a WS-1 classification is not feasible. WS-II waters are generally in predominantly
undeveloped watersheds. The supplemental classification of NSW denotes Nutrient
Sensitive Waters that require limitations on nutrient inputs. The WS-II classification for
predominately undeveloped watersheds is designated at the project study area.
Water Quality
The DWQ has initiated a basin-wide approach to water quality management for each of
the 17 river basins within the state. To accomplish this goal the DWQ collects biological,
chemical, and physical data that can be used in basinwide assessment and planning. All
basins are reassessed every five years. Prior to the implementation of the basinwide
approach to water quality management, the Benthic Macroinvertebrate Ambient Network
(BMAN, managed by the DEM) assessed water quality by sampling for benthic
macroinvertebrate organisms at fixed monitoring sites throughout the state. There is not
a BMAN station located on Quaker Creek within 1.6 kilometers (1.0 mile) of the project
study area.
Many benthic macroinvertebrates have stages in their life cycle that can last from six
months to a year, therefore, the adverse effects of a toxic spill will not be overcome until
the next generation. Different taxa of macroinvertebrates have different tolerances to
pollution, thereby, long-term changes in water quality conditions can be identified by
population shifts from pollution sensitive to pollution tolerant organisms (and vice versa).
Overall, the species present, the population diversity and the biomass are reflections of
long-term water quality conditions.
Point source dischargers located throughout North Carolina are permitted through the
National Pollutant Discharge Elimination System (NPDES) Program. Any discharger is
required to register for a permit. There is not a point source discharger located on Quaker
Creek within 1.6 kilometers (1.0 mile) of the project study area.
Summary of Anticipated Impacts
Replacing an existing structure in the same location with a road closure during
construction is almost always preferred. It poses the least risk to aquatic organisms and
other natural resources. Bridge replacement on a new location usually results in greater
impacts. Utilizing the full ROW width of 24.4 meters (80.0 feet), anticipated impacts to
Quaker Creek due to Alternate 1 will be 36.6m (120.0 feet). Alternate 1 impacts, both
aquatic and terrestrial, total 1.10 hectares (2.71 acres). The area of aquatic and terrestrial
environments impacted is 0.18 hectares (0.44 acres) and 0.92 ha (2.27 acres),
respectively. Alternate 2, utilizing the same ROW width could likely cause
approximately the same impacts as Alternate 1. Although the impact calculations show
approximately the same areas, Alternate 1 is preferred from an environmental standpoint
due to far fewer permanent impacts. Usually, project construction does not require the
entire right-of-way, therefore, actual impacts may be considerably less.
This project area is in the upper headwaters of the Graham-Mebane water supply
reservoir. The North Carolina Wildlife Resources Commission (WRC) requests that no
in-water work be performed from April 1 through June 15 due the quality largemouth
bass population that the lake supports. (WRC 1998)
Project construction may result in the following impacts to surface waters:
Increased sedimentation and siltation from construction and/or erosion,
2. Changes in light incidence and water clarity due to increased sedimentation and
vegetation removal,
3. Alteration of water levels and flows due to interruptions and/additions to surface
and ground water flow from construction,
4. Changes in water temperature due to streamside vegetation removal,
5. Increased nutrient loading during construction via runoff from exposed areas,
and/or
6. Increased concentration of toxic compounds from highway runoff, construction
and toxic spills.
Precautions must be taken to minimize impacts to water resources in the study area.
The NCDOT's Best Management Practices (BMP) for the Protection of Sensitive
Watersheds must be strictly enforced during the construction stage of the project.
Guidelines for these BMPs include, but are not limited to minimizing built upon
area and diverting stormwater away from surface water supply waters as much as
possible. Provisions to preclude contamination by toxic substances during the
construction interval must also be strictly enforced.
BIOTIC RESOURCES
Biotic resources include aquatic and terrestrial ecosystems. This section describes those
ecosystems encountered in the study area, as well as, the relationships between fauna and
flora within these ecosystems. Composition and distribution of biotic communities
throughout the project area are reflective of topography, hydrologic influences and past
and present land uses in the study area. Descriptions of the terrestrial systems are
presented in the context of plant community classifications and follow descriptions
presented by Schafale and Weakley (1990) where possible. Dominant flora and fauna
observed, or likely to occur, in each community are described and discussed.
Scientific nomenclature and common names (when applicable) are provided for each
animal and plant species described. Plant taxonomy generally follows Radford et al.
(1968). Animal taxonomy follows Martof et al. (1980), Potter et al. (1980) and Webster
et al. (1985). Subsequent references to the same organism will include the common name
only. Fauna observed during the site visits are denoted with an asterisk (*). Published
range distributions and habitat analysis are used in estimating fauna expected to be
present within the project area.
Terrestrial Communities
Four distinct terrestrial communities are identified in the project study area: Mesic Mixed
Hardwood Forest, maintained/disturbed community, yard and maintained/disturbed
roadside. Community boundaries within the study area are well defined without a
significant transition zone between them. Faunal species likely to occur within the study
area will exploit both communities for shelter and foraging opportunities or as movement
corridors.
Mesic Mixed Hardwood Forest
The Mesic Mixed Hardwood Forest is present along the entire project corridor. The
transition from forest to maintained/disturbed roadside community is abrupt due to road
shoulder maintenance activities.
The canopy is composed of red bud (Cercis canadensis), ash (Fraxinus sp.), hickory
(Carya sp.), poison ivy (Toxicodendron radicans), Japanese honeysuckle (Lonicera
japonica), Virginia pine (Pinus virginiana), red maple (Acer rubrum), beech (Fagus
grandifolia), hornbeam (Ostrya virginiana), white pine (Pinus strobus), yellow poplar
(Liriodendron tuplipifera), dogwood (Corpus jlorida), southern red oak (Quercus
falcata), white oak (Quercus alba), mulberry (Morus sp.), sugarberry (Celtis laevigata),
viburnum (Viburnum sp.), sassafras (Sassafras albidum), ironwood (Carpinus
caroliniana), American elm (Ulmus americana), black cherry (Prunus serotina), coral
honeysuckle (Lonicera sempervirens), winged sumac (Rhus copallina), Christmas fern
(Polystichum acrostichoides), kudzu (Pueraria lobata), Eastern red cedar (Juniperus
virginiana), wild rose (Rosa carolina) and willow oak (Quercus virginiana).
Wildlife associated with the Mesic Mixed Hardwood Forest include: white-tailed deer
(Odocoileus virginianus), eastern mole (Scalopus aquaticus), opossum (Didelphis
marsupialis), deer mouse (Peromyscus maniculatus), gray squirrel (Sciurus carolinensis),
beaver* (Castor canadensis), and raccoon (Procyon lotor). White-tailed deer will use
this forest community for cover and will forage on twigs and leaves as well as mast.
Avian species utilizing the alluvial forest include red-shouldered hawk (Buteo lineatus),
blue jay (Cyanocitta cristata), northern cardinal (Cardinalis cardinalis), rufous-sided
towhee (Pipilo erythrophthalmus), summer tanager (Piranga rubra), tufted titmouse
(Parus bicolor) and white-eyed vireo (Vireo griseus).
Maintained/ Disturbed Community
The maintained/disturbed community includes an area southwest of Bridge No. 60,
adjacent to Quaker Creek. Flora within this periodically maintained community is
primarily grass (Cynodon dactylon). The maintained habitat within the project area is
surrounded by extensive forested areas and represents only a minor constituent of a larger
community structure within the project vicinity. Therefore, faunal species frequenting
the maintained community will be largely those species inhabiting the Mesic Mixed
Hardwood Forest.
Maintained Yard
This maintained yard community includes lawns along SR 1921, west of Bridge No. 60.
This maintained community is comprised mostly of fescue grass (Festuca sp.).
The maintained habitat within the project area is surrounded by extensive forested areas
and represents only a minor constituent of a larger community structure within the project
vicinity. Therefore. faunal species frequenting the maintained community will be largely
those species inhabiting the Mesic Mixed Hardwood Forest.
Maintained/Disturbed Roadside Community
The maintained/disturbed roadside includes road shoulders along SR 1921 that are
present along the entire length of the project. Flora within this periodically maintained
community includes fescue (Festuca sp. ), chickweed (Stellaria media), field garlic
(Allium vineale), dock (Rumex crispus), Japanese honeysuckle, field pansy (Viola check
sp rafinesguii), henbit (Lamium amplexicaule), trumpet creeper (Campsis radicans), wild
strawberry (Fragaria virginiana) and vetch (Vicia angustifolia). The width of the road
shoulder is approximately 3.0 meters (10.0 feet).
The maintained habitat within the project area is surrounded by extensive forested areas
and represents only a minor constituent of a larger community structure within the project
vicinity. Therefore, faunal species frequenting the maintained community will be largely
those species inhabiting the Mesic Mixed Hardwood Forest.
Aquatic Communities
One aquatic community, Quaker Creek will be impacted by the proposed project.
Physical characteristics of a water body and the condition of the water resource influence
faunal composition of aquatic communities. Terrestrial communities adjacent to a water
resource also greatly influence aquatic communities
Fauna associated with these aquatic communities includes various invertebrate and
vertebrate species. Fish species likely to occur in Quaker Creek include golden shiner
(Notemigonus crysoleucas), creek chub (Semotilus atromaculatus), silver red-horse
(Moxostoma anisurum) and channel catfish (ktalurus punctatus). Invertebrates that
would be present include various species of caddisflies (Trichoptera), mayflies
(Ephemeroptera), crayfish (Decapoda), dragonflies (Odonata) and damselflies (Odonata).
The snapping turtle (Chelydra serpentina), pickerel frog (Rana palustris), and northern
water snake (Nerodia sipedon) are common residents in this community.
Summary of Anticipated Impacts
Construction of the subject project will have various impacts on the biotic resources
described. Any construction related activities in or near these resources have the
potential to impact biological functions. This section quantifies and qualifies impacts to
the natural resources in terms of area impacted and ecosystems affected. Temporary and
permanent impacts are considered here as well.
Calculated impacts to terrestrial resources reflect the relative abundance of each
community present within the study area. Project construction will result in clearing and
degradation of portions of these communities. Table 2 summarizes potential quantitative
losses to these biotic communities, resulting from project construction. Estimated
impacts are derived using the entire proposed right-of-way width of 24.4 meters (80.0
feet) along the project's 365.8 meters (1,200.0 feet) length, minus the area previously
impacted by the existing road. Although the impact calculations show approximately the
same areas, Alternate 1 is recommended due to far fewer permanent impacts. Usually,
project construction does not require the entire right-of-way, therefore, actual impacts
may be considerably less.
9
Table 2. Anticipated impacts from the proposed nroiect to biotic communities.
Community Alternate 1 Alternate 2
Mesic Mixed Hardwood Forest 0.51(l.25) 0.51(l.25)
Maintained/Disturbed Community 0.01 (0.03) 0.01 (0.03)
Yard 0.20 (0.48) 0.20 (0.48)
Maintained/Disturbed Roadside 0.20 (0.51) 0.20 (0.51)
Total 0.92 (2.27) 0.92 (2.27)
Note: Values cited are in hectares (acres).
Plant communities found within the proposed project area serve as nesting and sheltering
habitat for various wildlife species. Replacing Bridge No. 60 and its associated
improvements will reduce habitat for faunal species, thereby diminishing faunal numbers.
However, due to the size and scope of this project, it is anticipated that impacts to fauna
will be minimal.
Areas modified by construction (but not paved) will become road shoulders and early
successional habitat. Reduced habitat will displace some wildlife further from the
roadway while attracting other wildlife by the creation of earlier successional habitat.
Animals temporarily displaced by construction activities will repopulate areas suitable for
the species.
Aquatic communities are sensitive to even small changes in their environment. Stream
channelization, scouring, siltation, sedimentation and erosion from construction- related
work will affect water quality and biological constituents. Although direct impacts may
be temporary, environmental impacts from these construction processes may result in
long term or irreversible effects.
Impacts often associated with in-stream construction include increased channelization
and scouring of the streambed. In-stream construction alters the stream substrate and
may remove streamside vegetation at the site. Disturbances to the substrate will produce
siltation, which clogs the gills and/or feeding mechanisms of benthic organisms (sessile
filter-feeders and deposit-feeders), fish and amphibian species. Benthic organisms can
also be covered by excessive amounts of sediment. These organisms are slow to recover
or repopulate a stream.
The removal of streamside vegetation and placement of fill material at the construction
site alters the terrain. Alterations of the streambank enhance the likelihood of erosion and
sedimentation. Revegetation stabilizes and holds the soil thus mitigating these processes.
Erosion and sedimentation carry soils, toxic compounds and other materials into aquatic
communities at the construction site. These processes magnify turbidity and can cause
the formation of sandbars at the site and downstream, thereby altering water flow and the
growth of vegetation. Streamside alterations also lead to more direct sunlight penetration
and to elevations of water temperatures that may impact many species.
10
JURISDICTIONAL TOPICS
Waters of the United States
Surface waters and wetlands fall under the broad category of "waters of the United
States," as defined in Section 33 of the Code of Federal Register (CFR) Part 328.3.
Wetlands, defined in 33 CFR 328.3, are those areas that are inundated or saturated by
surface or ground water at a frequency and duration sufficient to support, and under
normal circumstances do support, a prevalence of vegetation typically adapted to life in
saturated conditions. Any action that proposes to place fill into these areas falls under the
jurisdiction of the U.S. Army Corps of Engineers (COE) under Section 404 of the Clean
Water Act (33 USC 1344).
Characteristics of Wetlands and Surface Waters
Potential wetland communities were investigated pursuant to the 1987 Corps of
Engineers Wetlands Delineation Manual. The three-parameter approach is used where
hydric soils, hydrophytic vegetation and prescribed hydrologic characteristics must all be
present for an area to be considered a wetland. Wetlands are not present within the project
area.
Quaker Creek is a jurisdictional surface water under Section 404 of the Clean Water Act
(33 USC 1344). Discussion of the biological, physical and water quality aspects of all
surface waters in the project area are presented in previous sections of this report.
Summary of Anticipated Impacts
Anticipated impacts to surface waters are determined by using the entire project ROW
width of 24.4 meters (80.0 feet). Considering Alternate 1, impacts to Quaker Creek will
consist of 36.6 meters (120.0 feet) wide and 39.6 meters (130 feet) long bridge crossing
of Quaker Creek, for an area of 0.14 ha (0.36 acre). Alternative 2 impacts to Quaker
Creek will be approximately the same as Alternate 1 impacts. Although the impact
calculations show approximately the same areas, Alternate 1 is preferred from an
environmental standpoint due to far fewer permanent impacts. Usually, project
construction does not require the entire ROW, therefore, actual surface water impacts
may be considerably less.
Permits
As described above, impacts to jurisdictional surface waters are anticipated from the
proposed project. As a result, construction activities will require permits and
certifications from various regulatory agencies charged with protecting the water quality
of public water resources
Nationwide Permit 23 (33 CFR 330.5(a) (23)) is likely to be applicable for all impacts to
"waters of the United States" resulting from the proposed project. This permit authorizes
activities undertaken, assisted, authorized, regulated, funded or financed in whole or part
by another federal agency or department where that agency or department has determined
that pursuant to the Council on Environmental Quality regulation for implementing the
procedural provisions of the National Environmental Policy Act the activity, work, or
discharge is categorically excluded from environmental documentation because it is
included within a category of actions which neither individually nor cumulatively have a
significant effect on the human environment, and that the office of the Chief of Engineers
has been furnished notice of the agency's or department's application for the categorical
exclusion and concurs with that determination.
This project will also require a 401 Water Quality Certification from the DWQ prior to
the issuance of the Nationwide Permit. Section 401 of the Clean Water Act requires that
the state issue or deny water certification for any federally permitted or licensed activity
that may result in a discharge to "waters of the United States." Section 401 Certification
allows surface waters to be temporarily impacted for the duration of the construction or
other land manipulation. The issuance of a 401 permit from the DWQ is a prerequisite to
issuance of a Section 404 permit.
Mitigation
The COE has adopted, through the Council on Environmental Quality (CEQ), a wetland
mitigation policy which embraces the concept of "no net loss of wetlands" and
sequencing. The purpose of this policy is to restore and maintain the chemical,
biological, and physical integrity of "waters of the United States," specifically wetlands.
Mitigation of wetland impacts has been defined by the CEQ to include: avoiding impacts
(to wetlands), minimizing impacts, rectifying impacts, reducing impacts over time and
compensating for impacts (40 CFR 1508.20). Each of these three aspects (avoidance,
minimization and compensatory mitigation) must be considered sequentially.
Avoidance
Avoidance mitigation examines all appropriate and practicable possibilities of averting
impacts to "waters of the United States." According to a 1990 Memorandum of
Agreement (MOA) between the Environmental Protection Agency (EPA) and the COE,
in determining "appropriate and practicable" measures to offset unavoidable impacts,
such measures should be appropriate to the scope and degree of those impacts and
practicable in terms of cost, existing technology and logistics in light of overall project
purposes.
Minimization
Minimization includes the examination of appropriate and practicable steps to reduce the
adverse impacts to "waters of the United States." Implementation of these steps will be
required through project modifications and permit conditions. Minimization typically
focuses on decreasing the footprint of the proposed project through the reduction of
median widths, ROW widths, fill slopes and/or road shoulder widths. Other practical
mechanisms to minimize impacts to "waters of the United States" crossed by the
proposed project include: strict enforcement of sedimentation control BMP's for the
protection of surface waters during the entire life of the project; reduction of clearing and
grubbing activity; reduction/elimination of direct discharge into streams; reduction of
runoff velocity; re-establishment of vegetation on exposed areas; judicious pesticide and
herbicide usage; minimization of "in-stream" activity; and litter/debris control.
Compensatory Mitigation
Compensatory mitigation is not normally considered until anticipated impacts to "waters
of the United States" have been avoided and minimized to the maximum extent
practicable. It is recognized that "no netToss of wetlands" functions and values may not
be achieved in each and every permit action. Appropriate and practicable compensatory
mitigation is required for unavoidable adverse impacts which remain after all appropriate
and practicable minimization has been performed. Compensatory actions often include
restoration, creation and enhancement of "waters of the United States." Such actions
12
should be undertaken in areas adjacent to or contiguous to the discharge site whenever
practicable. Compensatory mitigation is not usually necessary with a Nationwide Permit
No. 23.
Rare and Protected Species
Some populations of fauna and flora have been in, or are in, the process of decline either
due to natural forces or their inability to coexist with human activities. Federal law
(under the provisions of the Endangered Species Act of 1973, as amended) requires that
any action, likely to adversely affect a species classified as federally protected, be subject
to review by the U.S. Fish and Wildlife Service (FWS). Other species may receive
additional protection under separate state laws.
Federally-Protected Species
Plants and animals with federal classifications of Endangered (E), Threatened (T),
Proposed Endangered (PE), and Proposed Threatened (PT) are protected under the
provisions of Section 7 and Section 9 of the Endangered Species Act of 1973, as
amended. As of 13 March 2000 the FWS listed no federally protected species for
Alamance County.
Federal Species of Concern and State Listed Species
There are two Federal Species of Concern (FSC) listed for Alamance County. Federal
Species of Concern are not afforded federal protection under the ESA and are not subject
to any of its provisions, including Section 7, until they are formally proposed or listed as
Threatened or Endangered. Federal Species of Concern are defined as those species that
may or may not be listed in the future. These species were formally candidate species, or
species under consideration for listing for which there was insufficient information to
support a listing of Endangered, Threatened, Proposed Endangered and Proposed
Threatened. Organisms which are listed as Endangered (E), Threatened (T), Significantly
Rare (SR) or Special Concern (SC) by the North Carolina Natural Heritage Program
(NCNHP) list of rare plant and animal species are afforded state protection under the
State Endangered Species Act and the North Carolina Plant Protection and Conservation
Act of 1979.
Table 3 lists Federal Species of Concern , the species' state status (if afforded state
protection) and the existence of suitable habitat for each species in the study area. This
species list is provided for information purposes as the status of these species may be
upgraded in the future.
Table 3 Federal Species of Concern for Alamance County
Scientific Name Common Name State Status Habitat
Lam sills cariosa Yellow Lam mussel T Yes
Monotro sis odorata Sweet Pinesa C Yes
"T"----- A Threatened species is one which is likely to become an endangered species
within the foreseeable future throughout all or a significant portion of its range.
"C"----- A Candidate species is one which is very rare in North Carolina, generally with
1-20 populations in the state, generally substantially reduced in numbers by habitat
destruction, direct exploitation or disease. The species is also either rare throughout its
range or disjunct in North Carolina from a main range in a different part of the country or
the world.
13
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r North Carolina
Department of Transportation
Division of Highways
Planning & Environmental Branch
Alamance County
Replace Bridge No. 60 on SR 1921
Over Quaker Creek
W401
I FIGURE 1
Looking West Across
Bridge No. 60
Looking East Across
Bridge No. 60
,4 'of NO?TN'\ North Carolina Department of
T
ti
t
h ranspor
a
on
Division of Highways
Project Development &
1.9 Environmental Analysis Branch
Alamance County
Replace Bridge No. 60 on SR 1921
Over Quaker Creek
B-3401
Figure Three
'?
t
North Carolina Department of Cultural Resources
James B. Hunt Jr., Governor
Betty Ray McCain, Secretary
December 28, 1998
Nicholas L. Graf
Division Administrator
Federal Highway Administration
Department of Transportation
310 New Bern Avenue
Raleigh, N.C. 27601-1442
Re: Bridge #60 on SR 1921 over Quaker Creek,
Alamance County, B-3401, ER 99-7699
Dear Mr. Graf:
Division of Archives and History
Jeffrey J. Crow, Director
r' tee.
On December 15, 1998, Debbie Bevin of our staff met with North Carolina
Department of Transportation (NCDOT) staff for a meeting of the minds concerning
the above project. We reported our available information on historic architectural
and archaeological surveys and resources along with our recommendations.
NCDOT provided project area photographs and aerial photographs at the meeting.
Based upon our review of the photographs and the information discussed at the
meeting, we offer our preliminary comments regarding this project.
In terms of historic architectural resources, we are aware of no historic structures
located within the area of potential effect. We recommend that no historic
architectural survey be conducted for this project.
There are no known archaeological sites within the proposed project area. Based
on our present knowledge of the area, it is unlikely that any archaeological
resources which may be eligible for inclusion in the National Register of Historic
Places will be affected by the project construction. We, therefore, recommend that
no archaeological investigation be conducted in connection with this project.
Having provided this information, we look forward to receipt of either a Categorical
Exclusion or Environmental Assessment which indicates how NCDOT addressed our
comments.
The above comments are made pursuant to Section 106 of the National Historic
Preservation Act of 1966 and the Advisory Council on Historic Preservation's
Regulations for Compliance with Section 106, codified at 36 CFR Part 800.
A
10
02
Nicholas L. Graf
12/28/98, Page 2
Thank you for your cooperation and consideration. If you have questions
concerning the above comment, please contact Renee Gledhill-Earley, environmental
review coordinator, at 919/733-4763.
Sincerely,
David Brook
Deputy State Historic Preservation Officer
DB:slw
?
cc: W. D. Gilmore
B. Church
T. Padgett
/4
® North Carolina Wildlife Resources Commission
312 N. Salisbury Street, Raleigh, North Carolina 27604-1188, 919-733-3391
Charles R. Fullwood, Executive Director
MEMORANDUM
TO: John Williams, Project Planning Engineer
Planning & Environmental Branch, NCDOT
FROM: David Cox, Highway Project C rdina r -
Habitat Conservation Progr
DATE: December 21, 1998
SUBJECT: NCDOT Bridge Replacements in Alamance, Haywood, and Warren
counties, North Carolina. TIP Nos. B-3400, B-3401, B-3186, and
B-3532.
Biologists with the N. C. Wildlife Resources Commission (NCWRC) have
reviewed the information provided and have the following preliminary comments on the
subject project. Our comments are provided in accordance with provisions of the
National Environmental Policy Act (42 U.S.C. 4332(2)(c)) and the Fish and Wildlife
Coordination Act (48 Stat. 401, as amended; 16 U.S.C. 661-667d).
On bridge replacement projects of this scope our standard recommendations are as
follows:
1. We generally prefer spanning structures. Spanning structures usually do not
require work within the stream and do not require stream channel realignment.
The horizontal and vertical clearances provided by bridges allows for human
and wildlife passage beneath the structure, does not block fish passage, and
does not block navigation by canoeists and boaters.
2. Bridge deck drains should not discharge directly into the stream.
3. Live concrete should not be allowed to contact the water in or entering into the
stream.
4. If possible, bridge supports (bents) should not be placed in the stream.
Bridge Replacement Memo 2 December 21, 1998
5. If temporary access roads or detours are constructed, they should be removed
back to original ground elevations immediately upon the completion of the
project. Disturbed areas should be seeded or mulched to stabilize the soil and
native tree species should be planted with a spacing of not more than 10'x10'.
If possible, when using temporary structures the area should be cleared but not
grubbed. Clearing the area with chain saws, mowers, bush-hogs, or other
mechanized equipment and leaving the stumps and root mat intact, allows the
area to revegetate naturally and minimizes disturbed soil.
6. A clear bank (riprap free) area of at least 10 feet should remain on each side of
the steam underneath the bridge.
7. In trout waters, the N.C. Wildlife Resources Commission reviews all U.S.
Army Corps of Engineers nationwide and general `404' permits. We have the
option of requesting additional measures to protect trout and trout habitat and
we can recommend that the project require an individual '404' permit.
8. In streams that contain threatened or endangered species, NCDOT biologist
Mr. Tim Savidge should be notified. Special measures to protect these
sensitive species may be required. NCDOT should also contact the U.S. Fish
and Wildlife Service for information on requirements of the Endangered
Species Act as it relates to the project.
9. In streams that are used by anadromous fish, the NCDOT official policy
entitled "Stream Crossing Guidelines for Anadromous Fish Passage (May 12,
1997)" should be followed.
10. In areas with significant fisheries for sunfish, seasonal exclusions may also be
recommended.
If corrugated metal pipe arches or concrete box culverts are used:
1. The culvert must be designed to allow for fish passage. Generally, this means
that the culvert or pipe invert is buried at least 1 foot below the natural stream
bed. If multiple cells are required the second and/or third cells should be
placed so that their bottoms are at stream bankful stage (similar to Lyonsfield
design). This will allow sufficient water depth in the culvert or pipe during
normal flows to accommodate fish movements. If culverts are long, baffle
systems are required to trap gravel and provide resting areas for fish and other
aquatic organisms.
2. If multiple pipes or cells are used, at least one pipe or box should be designed
to remain dry during normal flows to allow for wildlife passage.
3. Culverts or pipes should be situated so that no channel realignment or
widening is required. Widening of the stream channel at the inlet or outlet of
structures usually causes a decrease in water velocity causing sediment
deposition that will require future maintenance.
4. Riprap should not be placed on the stream bed.
In most cases, we prefer the replacement of the existing structure at the same
location with road closure. If road closure is not feasible, a temporary detour should be
designed and located to avoid wetland impacts, minimize the need for clearing and to
Bridge Replacement Memo 3 December 21, 1998
avoid destabilizing stream banks. If the structure will be on a new alignment, the old
structure should be removed and the approach fills removed from the 100-year
floodplain. Approach fills should be removed down to the natural ground elevation. The
area should be stabilized with grass and planted with native tree species. If the area that
is reclaimed was previously wetlands, NCDOT should restore the area to wetlands. If
successful, the site may be used as wetland mitigation for the subject project or other
projects in the watershed.
Project specific comments:
1. B-3400 - No specific concerns.
2. B-3401 - This project is in the upper headwaters of the Graham-Mebane water
supply reservoir. This lake supports a diverse reservoir fishery with a quality
largemouth bass population. We request that no in-water work be performed
_frQm April 1 to June 15. _ _
3. B-3186 - Richland Creek is a tributary to Lake Junaluska. This section of
stream contains trout and is designated as Delayed Harvest Trout Waters. We
recommend that the existing structure be replaced with a bridge that spans the
entire stream. Although we do not request a seasonal exclusion for this
bridge, we do request that NCDOT use sedimentation and erosion control
measures for High Quality Waters. We also want to reiterate that NCDOT
should impress upon its contractors and inspectors that they are working in
streams which are public resources and extra care should be taken to insure
that sedimentation and erosion control devices are installed and maintained
properly.
4. B-3057 - No specific fishery concerns. However, there is the potential for
federally listed mussels to occur in the project vicinity. We recommend that
NCDOT biologists be contacted and a survey conducted. If mussels are
found, a field meeting should be held to discuss special measures to minimize
impacts to these animals.
We request that NCDOT routinely minimize adverse impacts to fish and wildlife
resources in the vicinity of bridge replacements. The NCDOT should install and
maintain sedimentation control measures throughout the life of the project and prevent
wet concrete from contacting water in or entering into these streams. Replacement of
bridges with spanning structures of some type, as opposed to pipe or box culverts, is
recommended in most cases. Spanning structures allow wildlife passage along
streambanks, reducing habitat fragmentation and vehicle related mortality at highway
crossings.
If you need further assistance or information on NCWRC concerns regarding
bridge replacements, please contact me at (919) 528-9886. Thank you for the opportunity
to review and comment on these projects.
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