20200688 Ver 1_00_Cornelius_PCN_JD_Complete_Optimized_20200522

Preliminary ORM Data Entry Fields for New Actions
ACTION ID #: SAW- Begin Date (Date Received):
Prepare file folder Assign Action ID Number in ORM
1. Project Name [PCN Form A2a]:
2. Work Type: Private Institutional Government Commercial
3. Project Description / Purpose [PCN Form B3d and B3e]:
4. Property Owner / Applicant [PCN Form A3 or A4]:
5. Agent / Consultant [PNC Form A5 – or ORM Consultant ID Number]:
6. Related Action ID Number(s) [PCN Form B5b]:
7. Project Location – Coordinates, Street Address, and/or Location Description [PCN Form B1b]:
8. Project Location – Tax Parcel ID [PCN Form B1a]:
9. Project Location – County [PCN Form A2b]:
10. Project Location – Nearest Municipality or Town [PCN Form A2c]:
11. Project Information – Nearest Waterbody [PCN Form B2a]:
12. Watershed / 8-Digit Hydrologic Unit Code [PCN Form B2c]:
Authorization: Section 10 Section 404 Section 10 and 404
Regulatory Action Type:
Pre-Application Request
Unauthorized Activity
Compliance
Standard Permit
Nationwide Permit #








Regional General Permit #
Jurisdictional Determination Request No Permit Required
Revised 20150602
27
Upper McDowell Creek Tributary Stream Restoration
✔
This application is to request authorization to conduct stream bank stabilization and in-stream enhancement activities for the purposes
of improving water quality, bank stabilization, and aquatic habitat. This submittal is to request a PJD and submit PCN pursuant to
NWP 27 for the Willow Pond Stream Restoration project (Figure 1).
Town of Cornelius
Chris Tinklenberg, PWS (Kimley-Horn)
N/A
The subject property is located from Westmoreland Road to Catawba Avenue in the Town of Cornelius,
Mecklenburg County (Figure 1). Project Coordinates (Decimal Degrees): 35.470624 N, -80.871835 W.
N/A
Mecklenburg
Cornelius
McDowell Creek
Catwaba (HUC 03050101)
✔
✔
✔

kimley-horn.com 200 South Tryon Street, Suite 200, Charlotte, NC 28202 704-333-5131

May 22, 2020

Mr. David Shaeffer
Asheville Regulatory Field Office
US Army Corps of Engineers
151 Patton Avenue, Room 208
Asheville, NC 28801-5006

Ms. Karen Higgins
NC DWR, 401 & Buffer Permitting Unit
512 North Salisbury Street
Raleigh, NC 27604

Re: Pre-Construction Notification (NWP 27) &
Preliminary Jurisdictional Determination Request
Upper McDowell Creek Tributary Stream Restoration
Cornelius, Mecklenburg County, NC

Dear Mr. Shaeffer and Ms. Higgins:

On behalf of our client, Town of Cornelius, Kimley-Horn (KH) is submitting the enclosed joint Section 404/401 Pre-
Construction Notification for the above referenced project for your review pursuant to Nationwide Permit 27 and
General 401 Water Quality Certification number 4134 as well as a Preliminary Jurisdictional Determination (JD)
request package for your review for the above referenced project. The subject property is situated between
Westmoreland Road to Catawba Avenue, in Cornelius, Mecklenburg County. Authorization is requested to conduct
stream restoration along McDowell Creek and three unnamed tributaries to McDowell Creek. The center of the
project area is located at 35.470624°N, -80.871835 °W. The following information is included as part of this
application submittal:

The following information is included as part of this application submittal:
Project Summary Sheet
Agent Authorization
Pre-Construction Notification Form
Jurisdictional Determination Request Form
Project Site Figures
Figure 1 – Vicinity
Figure 2 – USGS 7.5’ Topo (Lake Norman South; Cornelius)
Figure 3 – Meck. Co. SSURGO Soils (2019 Meck. Co. Aerial)
Figure 4 – PJD Field Sketch (2019 Meck. Co. Aerial)
Figure 5 – Proposed Conditions (2019 Meck. Co. Aerial)
Preliminary Plans of Proposed 5,175 linear feet of Stream Restoration
Project Site Photographs
Field Data Forms
NCDWR Stream Identification Forms
Wetland Determination Data Sheets
NCSAM Forms
Agency Correspondence

PROJECT DESCRIPTION

The Town of Cornelius proposes to perform stream restoration and enhancement activities along the McDowell
Creek and three unnamed tributaries to McDowell Creek within the project corridor. The proposed restoration
activities, such as bank stabilization and in-stream enhancements, seek to reduce bank erosion, improve
channel dimension, and stabilize bank areas in close proximity to the proposed greenway and multi-use path.
Stabilization includes bank grading to a stable slope, rock toe protection, and buffer revegetation. The project
Page 2
kimley-horn.com 200 South Tryon Street, Suite 200, Charlotte, NC 28202 704-333-5131

corridor begins from Highway 21 (south of Catawba Avenue) to north of J.V. Washam Elementary School and is
adjacent to McDowell Creek and three unnamed tributaries to McDowell Creek.

SITE DESCRIPTION

The project corridor is located in the piedmont region of North Carolina. Topography is moderate within the study
corridor and roughly ranges from 740 to 840 feet in elevation (Figure 2).

The project is located in the Catawba River Basin. A field review by Kimley-Horn environmental scientists was
conducted on October 24, 2018. McDowell Creek and three (3) unnamed tributaries (potential non-wetland
WoUS), and one (1) potential wetland WoUS are located within the project study corridor (Figures 4a-4b).

McDowell Creek is rated by the North Carolina Department of Environment and Natural Resources (NCDENR)
Division of Water Resources (DWR) as Class C with the following DWR Stream Index # 11-115-(1). Class C
waters are protected for primary recreation, fishing, wildlife, fish consumption, aquatic habitat and agricultural
uses. Currently, McDowell Creek is not classified as 303d listed, but is classified as a Level 4 Impaired Stream.
The project corridor does not lie within a Water Supply Watershed, however, a Water Supply Watershed
(Mountain Island Lake; WS-IV) exists within a mile downstream of the project corridor. There are no Outstanding
Resource Waters or High Quality Waters within the project corridor.

Stream 1 (S1) is a perennial stream that is a UT of McDowell Creek. It enters the project boundary in the
northern portion of the corridor and flow continues south for 1,047 linear feet, where it flows into a open water
pond (Willow Pond). Willow Pond (OW1) appears to be an in-line man-made impoundment that was constructed
between 1960 and 1965. S1 outfalls from the pond and continues flowing south for 1,269 linear feet until it flows
into McDowell Creek. McDowell Creek (S2) is a perennial stream that flows into the project corridor on the
eastern boundary and flows directly west until it leaves the project corridor, culverted under Statesville Road.
Stream 3 (S3) enters into the project boundary and flows north for about 696 linear feet until it reaches its
confluence with McDowell Creek. Stream 4 (S4) is a rip-rap lined intermittent stream that enters the project
corridor and is mostly influenced by stormwater drainage discharge from the surrounding neighborhood. S4 flows
225 linear feet southwest until it reaches it confluence with S3. Wetland 1 is a 0.24-acre wetland that exists in the
floodplain of S3.

STREAM REHABILITATION APPROACH

Goals and Objectives:
The goal of the stream and buffer rehabilitation is to improve the hydraulic and geomorphic function of McDowell
Creek and the three unnamed tributaries to create a foundation for potential improvements of water quality and
aquatic/terrestrial habitat of the site’s streams and floodplain. The existing dam to OW1 will be breached,
allowing the S1 to reform in the existing pond bed and restore OW1 to its previous stream form. Improvements in
the higher functions of water quality and biology may not be fully achievable given the upstream urban land use
and point and non-point discharges. However, improving the underlying stream hydraulic and geomorphic
functions of the channel would better support these improvements in higher functions if watershed conditions
allow. Based on the objectives above, a specific detailed stream rehabilitation plan was completed. Each reach
has a tailored approach/plan that takes advantage of the opportunities to improve geomorphic and hydraulic
functions given the constraints.

To meet the goals and objectives described above, stream enhancement and restoration activities will be
conducted, resulting in 4,533 linear feet of permanent, no-net loss of potential non-wetland WoUS. The project
will result in a total net gain of 642 linear feet to waters of the US from implementing natural channel design
techniques to return the channels to their natural bed and stabilizing erosive banks. 60 linear feet of temporary
impacts are requested to work in the dry.

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kimley-horn.com 200 South Tryon Street, Suite 200, Charlotte, NC 28202 704-333-5131

AVOIDANCE AND MINIMIZATION

All impacts are associated with stream restoration activities and will follow specific restoration protocols. The
project will result in a net gain of 642 linear feet to waters of the US from implementing natural channel design
techniques to return the channels to their natural bed and stabilizing erosive banks. Several of the measures that
will be implemented in order to minimize impacts include the utilization of a pumped diversion to facilitate work in
the dry, the use of temporary erosion control matting and planting of native vegetation for stabilization. The
pumped diversion will be utilized for working in the dry to the greatest extents practicable; however, some
construction activities may require the contractor to temporarily work in the wet. Please provide special
conditions authorizing the contractor to work in the wet where a pumped diversion is not feasible. All
sediment and erosion control and de-watering measures will be removed upon completion of construction and
the temporary areas of disturbance will be stabilized and restored to pre-construction contours. Impacts to
wetlands have been avoided within the project corridor.

Please feel free to contact me at [phone] if you have any questions or if additional information is necessary.

Sincerely,

KIMLEY-HORN AND ASSOCIATES, INC.

Chris Tinklenberg, PWS
Environmental Scientist

Attachments

Cc: Alan Johnson
Division of Water Resources
610 East Center Ave., Suite 301
Mooresville, NC 28115

Project Summary Sheet
kimley-horn.com 200 South Tryon Street, Suite 200, Charlotte, NC 28202 704-333-5131

Project Name: Upper McDowell Creek Tributary Stream Restoration
Applicant Name and Address: Tyler Beardsley, Town Assistant Manager / Public Works Director
Cornelius PARC Department
21445 Catawba Avenue
Cornelius, NC 28031
[e-mail]
Telephone Number: 704.892.6031 ext. 127
Type of Request: Nationwide PCN (NWP # 27) Individual Permit Application

Jurisdictional Determination Other:
Included Attachments: Project Plans USGS Map NRCS Soil Survey
Agent Authorization Delineation Sketch Delineation Survey
Data Forms (Up & Wet) NCDWR Stream Forms USACE Stream Forms
NCEEP Confirmation Aerial Photo Site Photos
Agency Correspondence Other: Other:
Check if applicable: CAMA County Trout County Isolated Waters
Section 7, ESA Section 106, NHPA EFH
Mitigation Proposed ( NC EEP On-Site Off-Site Other)
County: Mecklenburg Nearest City/Town: Cornelius
Waterway: McDowell Creek River Basin: Catawba
H.U.C.: 03050101 USGS Quad Name: Lake Norman South; Cornelius
Property Size (acres): ~64.6 acres Approx. Size of Jurisdiction on Site (acres):~ 2.65
Site Coordinates (in decimal degrees): 35.470624 °N -80.871835 °W
Project Location: The project corridor begins from Highway 21 (south of Catawba Avenue) to north of J.V. Washam
Elementary School adjacent to McDowell Creek and three unnamed tributaries to McDowell Creek in Cornelius, NC.

Site Description: Existing land use on the site include undeveloped mixed hardwood/pine forests, McDowell Creek and
three unnamed tributaries, as well as man-made pond

Impact Summary (if applicable):The project will result in 4,533 lf of permanent-no net loss stream impacts from the
restoration activities necessary to improve stream functions and reduce bank erosion. The project will result in a total net
gain of 642 lf of waters of the US from implementing natural channel design techniques to return the channels to their
natural bed and stabilizing erosive banks to McDowell Creek and three UTs to McDowell Creek. 60 lf of temporary impacts
are requested to work in the dry.

NWP
#
Open Water
(acres)
Wetland
(acres)
Stream Channel
Intermittent and/or Unimportant
Aquatic Function
Perennial and/or Important
Aquatic Function
Temp. Perm. Temp. Perm. Temp. Perm. Temp. Perm.
lf ac lf ac lf ac lf Ac
27 225 0.026 60 0.014 4,308 0.99
Total 225 0.026 60 0.014 4,308 0.99
Total Permanent Impact to Waters of the U.S. (feet/acres) 4,533 / 1.016
Total Net Gain to Waters of the U.S. (feet/acres) 642 / 0.15

Kimley-Horn Contact: Chris Tinklenberg, PWS Direct Number: [phone]
Email: [e-mail]
AGENT AUTHORIZATION
FORM
Name: lfflAW a/ 1j.P/Ip/ir,
Address: glyq�- �.6L6L�ka_ f Uel4ue;
Phone: D ^ 812 - 63 (
Email:
Project Name/Description: Upper McDowell Creek Tributary Stream Restoration
Date: s 21 m U
The Department of the Army
U.S. Army Corps of Engineers, Wilmington District
Attention: Mr. David Shaeffer
Field Office: Asheville Regulatory Field Office
Re: Wetland Related Consulting and Permitting
To Whom It May Concern: r
6 - r w vt 6V,he1r;by designates and authorizes Kimley-Horn and Associates,
Inc. to act in m /o r behalf as my/our agent solely for the purpose of processing Jurisdictional
Determinations, Section 404 permits/Section 401 Water Quality Certifications applications and
to furnish upon request supplemental information in support of applications, etc. from this day
forward until successful completion of the permitting process or revocation by the owner.
In addition, I, the undersigned, a duly authorized owner of record of the property/properties
identified herein, do authorize representatives of the Wilmington District, U.S. Army Corps of
Engineers (Corps) to enter upon the property herein described for the purpose of conducting on -
site investigations and issuing a determination associated with Waters of the U.S. subject to
Federal jurisdiction under Section 404 of the Clean Water Act and/or Section 10 of the Rivers
and Harbors Act of 1899.
Authorized this the �1 day of 61
Print Propeq Owner's Name roperty Owner gnature
Cc: Karen Higgins
NC Division of Water
Resources 401 & Buffer
Permitting Unit 1650
Mail Service Center
Raleigh, NC 27699-
1650

Page 1 of 11
PCN Form – Version 1.3 December 10, 2008 Version
Office Use Only:
Corps action ID no. _____________
DWQ project no. _______________
Form Version 1.3 Dec 10 2008
Pre-Construction Notification (PCN) Form
A. Applicant Information
1. Processing
1a. Type(s) of approval sought from the
Corps: Section 404 Permit Section 10 Permit
1b. Specify Nationwide Permit (NWP) number: 27 or General Permit (GP) number:
1c. Has the NWP or GP number been verified by the Corps? Yes No
1d. Type(s) of approval sought from the DWQ (check all that apply):
401 Water Quality Certification – Regular Non-404 Jurisdictional General Permit
401 Water Quality Certification – Express Riparian Buffer Authorization
1e. Is this notification solely for the record
because written approval is not required?

For the record only for DWQ 401
Certification:
Yes No
For the record only for Corps Permit:

Yes No
1f. Is payment into a mitigation bank or in-lieu fee program proposed for mitigation
of impacts? If so, attach the acceptance letter from mitigation bank or in-lieu
fee program.
Yes No

1g. Is the project located in any of NC’s twenty coastal counties? If yes, answer
1h below.
Yes No

1h. Is the project located within a NC DCM Area of Environmental Concern (AEC)? Yes No
2. Project Information
2a. Name of project: Upper McDowell Creek Tributary Stream Restoration
2b. County: Mecklenburg
2c. Nearest municipality / town: Cornelius
2d. Subdivision name: N/A
2e. NCDOT only, T.I.P. or state
project no: N/A
3. Owner Information
3a. Name(s) on Recorded Deed: N/A
3b. Deed Book and Page No.
3c. Responsible Party (for LLC if
applicable): Town of Cornelius
3d. Street address: P.O. Box 399
3e. City, state, zip: Cornelius, NC 28031
3f. Telephone no.:
3g. Fax no.:
3h. Email address:

Page 2 of 11
PCN Form – Version 1.3 December 10, 2008 Version

4. Applicant Information (if different from owner)
4a. Applicant is: Agent Other, specify: Public Agency
4b. Name: Tyler Beardsley, Town Assistant Manager / Public Works Director
4c. Business name
(if applicable): Cornelius PARC Department
4d. Street address: 21445 Catawba Avenue
4e. City, state, zip: Cornelius, NC 28031
4f. Telephone no.: P: 704.892.6031 ext. 127
4g. Fax no.:
4h. Email address: [e-mail]
5. Agent/Consultant Information (if applicable)
5a. Name: Chris Tinklenberg, PWS
5b. Business name
(if applicable): Kimley-Horn and Associates, Inc.
5c. Street address: 200 South Tryon Street, Suite 200
5d. City, state, zip: Charlotte, NC 28202
5e. Telephone no.: 704-409-1802
5f. Fax no.:
5g. Email address: [e-mail]

Page 3 of 11
PCN Form – Version 1.3 December 10, 2008 Version

B. Project Information and Prior Project History
1. Property Identification
1a. Property identification no. (tax PIN or parcel ID): N/A
1b. Site coordinates (in decimal degrees): Latitude: 35.470624 Longitude: -80.871835
(DD.DDDDDD) (-DD.DDDDDD)
1c. Property size: 64.6 acre
2. Surface Waters
2a. Name of nearest body of water (stream, river, etc.) to
proposed project: McDowell Creek
2b. Water Quality Classification of nearest receiving water: “C”
2c. River basin: Catawba
3. Project Description
3a. Describe the existing conditions on the site and the general land use in the vicinity of the project at the time of this
application:
The project corridor begins from Highway 21 (south of Catawba Avenue) to north of J.V. Washam Elementary School
adjacent to McDowell Creek and two unnamed tributaries to McDowell Creek. Existing land use on the site include
undeveloped mixed hardwood/pine forests, McDowell Creek and three unnamed tributaries, as well as man-made pond.
Existing land use in the vicinity of the project includes single- family residential developments, mixed hardwood/pine
forest, cleared utility easement, a greenway, and two community parks.
3b. List the total estimated acreage of all existing wetlands on the property:
NA
3c. List the total estimated linear feet of all existing streams (intermittent and perennial) on the property:
~4,533 lf of existing stream in the project boundary
3d. Explain the purpose of the proposed project:
The purpose of the project is to conduct stream restoration along McDowell Creek and three unnamed tributaries to
McDowell Creek by implementing natural channel design.
3e. Describe the overall project in detail, including the type of equipment to be used:
Stream restoration will utilize natural channel design techniques to address the instabilities within the stream channels. In-
stream structures, including boulder sills, constructed riffles, and step pools will be used to create grade control, provide
in-stream habitat, enhance aquatic life passage through the project area and to help protect the banks. Overall, the
design seeks to stabilize the channels, reduce erosion, elevate the channel beds, improve in-stream habitat and
geomorphology, alleviate residential flooding, and replace/protect the utilities. The existing dam to OW1 will be breached,
allowing the S1 to reform in the existing pond bed and restore OW1 to its previous stream form. It is anticipated that a
back-hoe and/or mini excavator will be used to shape the channels and construct the in-stream structures. Pumped
diversions will be utilized for working in the dry to the greatest extents practicable; however, some construction activities
may require the contractor to temporarily work in the wet.
4. Jurisdictional Determinations
4a. Have jurisdictional wetland or stream determinations by the
Corps or State been requested or obtained for this property /
project (including all prior phases) in the past?
Comments:
Yes No Unknown
4b. If the Corps made the jurisdictional determination, what type
of determination was made? Preliminary Final
4c. If yes, who delineated the jurisdictional areas?
Name (if known):
Agency/Consultant Company:
Other:
4d. If yes, list the dates of the Corps jurisdictional determinations or State determinations and attach documentation.

Page 4 of 11
PCN Form – Version 1.3 December 10, 2008 Version

5. Project History
5a. Have permits or certifications been requested or obtained for
this project (including all prior phases) in the past? Yes No Unknown
5b. If yes, explain in detail according to “help file” instructions.

6. Future Project Plans
6a. Is this a phased project? Yes No
6b. If yes, explain.
The stream restoration project will occur in two phases.

C. Proposed Impacts Inventory
1. Impacts Summary
1a. Which sections were completed below for your project (check all that apply):
Wetlands Streams - tributaries Buffers
Open Waters Pond Construction

Page 5 of 11
PCN Form – Version 1.3 December 10, 2008 Version

2. Wetland Impacts
If there are wetland impacts proposed on the site, then complete this question for each wetland area impacted.
2a.
Wetland impact
number – Permanent
(P) or Temporary (T)
2b.

Type of impact
2c.

Type of
wetland
(if known)
2d.

Forested

2e.
Type of jurisdiction
(Corps - 404, 10
DWQ – non-404,
other)
2f.

Area of
impact
(acres)
2g. Total wetland impacts
2h. Comments:
3. Stream Impacts
If there are perennial or intermittent stream impacts (including temporary impacts) proposed on the site, then complete this
question for all stream sites impacted.
3a.
Stream impact number
-Permanent (P) or
Temporary (T)
3b.
Type of impact
3c.
Stream name
3d.
Perennial (PER)
or intermittent
(INT)?
3e.
Type of
jurisdiction
(Corps - 404,
10
DWQ – non-
404, other)
3f.
Average
stream
width
(feet)
3g.
Impact
length
(linear
feet)
S1 – UT to McDowell
Creek - Impact 1
P T
Restoration/Stabilization
UT to
McDowell
Creek
PER
INT
Corps
DWQ 10 2,316
S1 – UT to McDowell
Creek - Impact 2
P T
Installation of
Impervious Dike and
Pump Around
UT to
McDowell
Creek
PER
INT
Corps
DWQ 10 15
S2 – McDowell Creek -
Impact 3
P T
Restoration/Stabilization McDowell
Creek
PER
INT
Corps
DWQ 13 696
S2 – McDowell Creek -
Impact 4
P T
Installation of
Impervious Dike and
Pump Around
McDowell
Creek
PER
INT
Corps
DWQ 13 15
S3 – UT to McDowell
Creek - Impact 5
P T
Restoration/Stabilization
UT to
McDowell
Creek
PER
INT
Corps
DWQ 10 1,296
S3 – UT to McDowell
Creek - Impact 6
P T
Installation of
Impervious Dike and
Pump Around
UT to
McDowell
Creek
PER
INT
Corps
DWQ 10 15
S4 – UT to McDowell
Creek - Impact 7
P T
Restoration/Stabilization
UT to
McDowell
Creek
PER
INT
Corps
DWQ 5 225
S4 – UT to McDowell
Creek - Impact 8
P T
Installation of
Impervious Dike and
Pump Around
UT to
McDowell
Creek
PER
INT
Corps
DWQ 5 15

Page 6 of 11
PCN Form – Version 1.3 December 10, 2008 Version

3h. Total stream and tributary impacts 5,343
3i. Comments: Impacts associated with the stream enhancement and restoration activities will be conducted, resulting in
4,533 linear feet of permanent, no-net loss of potential non-wetland WoUS. The project will result in a total net gain of 642 lf to
waters of the US from implementing natural channel design techniques to return the channels to their natural bed and
stabilizing erosive banks. 60 lf of temporary impacts are requested to work in the dry.
4. Open Water Impacts
If there are proposed impacts to lakes, ponds, estuaries, tributaries, sounds, the Atlantic Ocean, or any other open water of
the U.S. then individually list all open water impacts below.
4a.
Open water
impact number –
Permanent (P) or
Temporary (T)
4b.
Name of waterbody
(if applicable)
4c.

Type of impact
4d.

Waterbody type
4e.

Area of impact (acres)
O1 P T
4f. Total open water impacts
4g. Comments:
5. Pond or Lake Construction
If pond or lake construction proposed, then complete the chart below.
5a.

Pond ID
number
5b.

Proposed use or purpose
of pond

5c.
Wetland Impacts (acres)
5d.
Stream Impacts (feet)
5e.
Upland
(acres)
Flooded Filled Excavated Flooded Filled Excavated Flooded
P1
P2
5f. Total
5g. Comments:
5h. Is a dam high hazard permit required?
Yes No If yes, permit ID no:
5i. Expected pond surface area (acres):
5j. Size of pond watershed (acres):
5k. Method of construction:

Page 7 of 11
PCN Form – Version 1.3 December 10, 2008 Version

6. Buffer Impacts (for DWQ)
If project will impact a protected riparian buffer, then complete the chart below. If yes, then individually list all buffer impacts
below. If any impacts require mitigation, then you MUST fill out Section D of this form.
6a.
Project is in which protected basin?
Neuse Tar-Pamlico Other:
Catawba Randleman
6b.
Buffer impact
number –
Permanent (P) or
Temporary (T)
6c.

Reason
for
impact
6d.

Stream name
6e.

Buffer
mitigation
required?
6f.

Zone 1 impact
(square feet)
6g.

Zone 2 impact
(square feet)
B1 P T Yes
No
B2 P T Yes
No
B3 P T Yes
No
6h. Total buffer impacts
6i. Comments:
D. Impact Justification and Mitigation
1. Avoidance and Minimization
1a. Specifically describe measures taken to avoid or minimize the proposed impacts in designing project.
All impacts are associated with stream restoration activities and will follow specific restoration protocols. The project will result
in a net gain of 642 lf to waters of the US from implementing natural channel design techniques to return the channels to their
natural bed and stabilizing erosive banks. Impacts to wetlands have been avoided within the project corridor
1b. Specifically describe measures taken to avoid or minimize the proposed impacts through construction techniques.
Several of the measures that will be implemented in order to minimize impacts include the utilization of a pumped diversion to
facilitate work in the dry, the use of temporary erosion control matting and planting of native vegetation for stabilization. The
pumped diversion will be utilized for working in the dry to the greatest extents practicable; however, some construction
activities may require the contractor to temporarily work in the wet. All sediment and erosion control and de-watering
measures will be removed upon completion of construction and the temporary areas of disturbance will be stabilized and
restored to pre-construction contours.
2. Compensatory Mitigation for Impacts to Waters of the U.S. or Waters of the State
2a. Does the project require Compensatory Mitigation for
impacts to Waters of the U.S. or Waters of the State?
Yes No

2b. If yes, mitigation is required by (check all that apply): DWQ Corps
2c. If yes, which mitigation option will be used for this
project?
Mitigation bank
Payment to in-lieu fee program
Permittee Responsible Mitigation
3. Complete if Using a Mitigation Bank
3a. Name of Mitigation Bank:
3b. Credits Purchased (attach receipt and letter) Type: Quantity:

Page 8 of 11
PCN Form – Version 1.3 December 10, 2008 Version

3c. Comments:
4. Complete if Making a Payment to In-lieu Fee Program
4a. Approval letter from in-lieu fee program is attached. Yes
4b. Stream mitigation requested:
4c. If using stream mitigation, stream temperature: warm cool cold
4d. Buffer mitigation requested (DWQ only): square feet
4e. Riparian wetland mitigation requested: acres
4f. Non-riparian wetland mitigation requested: acres
4g. Coastal (tidal) wetland mitigation requested: acres
4h. Comments:
5. Complete if Using a Permittee Responsible Mitigation Plan
5a. If using a permittee responsible mitigation plan, provide a description of the proposed mitigation plan.

6. Buffer Mitigation (State Regulated Riparian Buffer Rules) – required by DWQ
6a. Will the project result in an impact within a protected riparian buffer that requires
buffer mitigation?
Yes No

6b. If yes, then identify the square feet of impact to each zone of the riparian buffer that requires mitigation. Calculate the
amount of mitigation required.
Zone
6c.
Reason for impact
6d.
Total impact
(square feet)

Multiplier
6e.
Required mitigation
(square feet)
Zone 1 3 (2 for Catawba)
Zone 2 1.5
6f. Total buffer mitigation required:
6g. If buffer mitigation is required, discuss what type of mitigation is proposed (e.g., payment to private mitigation bank,
permittee responsible riparian buffer restoration, payment into an approved in-lieu fee fund).

6h. Comments:

Page 9 of 11
PCN Form – Version 1.3 December 10, 2008 Version

E. Stormwater Management and Diffuse Flow Plan (required by DWQ)
1. Diffuse Flow Plan
1a. Does the project include or is it adjacent to protected riparian buffers identified
within one of the NC Riparian Buffer Protection Rules? Yes No
1b. If yes, then is a diffuse flow plan included? If no, explain why.
Comments:
Yes No
2. Stormwater Management Plan
2a. What is the overall percent imperviousness of this project? 0 %
2b. Does this project require a Stormwater Management Plan? Yes No
2c. If this project DOES NOT require a Stormwater Management Plan, explain why:

2d. If this project DOES require a Stormwater Management Plan, then provide a brief, narrative description of the plan:

2e. Who will be responsible for the review of the Stormwater Management Plan?
Certified Local Government
DWQ Stormwater Program
DWQ 401 Unit
3. Certified Local Government Stormwater Review
3a. In which local government’s jurisdiction is this project?
3b. Which of the following locally-implemented stormwater management programs
apply (check all that apply):
Phase II
NSW
USMP
Water Supply Watershed
Other:
3c. Has the approved Stormwater Management Plan with proof of approval been
attached?
Yes No
4. DWQ Stormwater Program Review
4a. Which of the following state-implemented stormwater management programs apply
(check all that apply):
Coastal counties
HQW
ORW
Session Law 2006-246
Other:
4b. Has the approved Stormwater Management Plan with proof of approval been
attached? Yes No
5. DWQ 401 Unit Stormwater Review
5a. Does the Stormwater Management Plan meet the appropriate requirements? Yes No
5b. Have all of the 401 Unit submittal requirements been met? Yes No

Page 10 of 11
PCN Form – Version 1.3 December 10, 2008 Version

F. Supplementary Information
1. Environmental Documentation (DWQ Requirement)
1a. Does the project involve an expenditure of public (federal/state/local) funds or the
use of public (federal/state) land? Yes No
1b. If you answered “yes” to the above, does the project require preparation of an
environmental document pursuant to the requirements of the National or State
(North Carolina) Environmental Policy Act (NEPA/SEPA)?
Yes No
1c. If you answered “yes” to the above, has the document review been finalized by the
State Clearing House? (If so, attach a copy of the NEPA or SEPA final approval
letter.)
Comments:
Yes No
2. Violations (DWQ Requirement)
2a. Is the site in violation of DWQ Wetland Rules (15A NCAC 2H .0500), Isolated
Wetland Rules (15A NCAC 2H .1300), DWQ Surface Water or Wetland Standards,
or Riparian Buffer Rules (15A NCAC 2B .0200)?
Yes No
2b. Is this an after-the-fact permit application? Yes No
2c. If you answered “yes” to one or both of the above questions, provide an explanation of the violation(s):
3. Cumulative Impacts (DWQ Requirement)
3a. Will this project (based on past and reasonably anticipated future impacts) result in
additional development, which could impact nearby downstream water quality? Yes No
3b. If you answered “yes” to the above, submit a qualitative or quantitative cumulative impact analysis in accordance with the
most recent DWQ policy. If you answered “no,” provide a short narrative description.
The project objective is to conduct stream restoration and bank stabilization. These activities will not result in additional
development.
4. Sewage Disposal (DWQ Requirement)
4a. Clearly detail the ultimate treatment methods and disposition (non-discharge or discharge) of wastewater generated from
the proposed project, or available capacity of the subject facility.

Page 11 of 11
PCN Form – Version 1.3 December 10, 2008 Version

5. Endangered Species and Designated Critical Habitat (Corps Requirement)
5a. Will this project occur in or near an area with federally protected species or
habitat? Yes No
5b. Have you checked with the USFWS concerning Endangered Species Act
impacts? Yes No
5c. If yes, indicate the USFWS Field Office you have contacted.
Raleigh
Asheville
5d. What data sources did you use to determine whether your site would impact Endangered Species or Designated Critical
Habitat?
A review of North Carolina Natural Heritage Program Database on July 17, 2018 did not indicate any Endangered
Species or Designated Critical Habitat within project boundary. Pedestrian surveys were performed by Kimley-Horn staff
on October 17, 2018. No endangered species were identified during the survey.
6. Essential Fish Habitat (Corps Requirement)
6a. Will this project occur in or near an area designated as essential fish habitat? Yes No
6b. What data sources did you use to determine whether your site would impact Essential Fish Habitat?
North Carolina Natural Heritage Program Database
7. Historic or Prehistoric Cultural Resources (Corps Requirement)
7a. Will this project occur in or near an area that the state, federal or tribal
governments have designated as having historic or cultural preservation
status (e.g., National Historic Trust designation or properties significant in
North Carolina history and archaeology)?
Yes No
7b. What data sources did you use to determine whether your site would impact historic or archeological resources?
A review of the North Carolina State Historic Preservation Office (SHPO) HPOWEB GIS Service database did not
indicate any cultural or historic resources within the project boundary. Additionally, a response received from North
Carolina Department of Natural and Cultural Resources on August 16, 2018 states that no historic resources would be
affected by the project.
8. Flood Zone Designation (Corps Requirement)
8a. Will this project occur in a FEMA-designated 100-year floodplain? Yes No
8b. If yes, explain how project meets FEMA requirements: A flood impact analysis report, no-rise certification, and individual
floodplain development permit will be submitted to Mecklenburg County for review and approval prior to
construction/restoration activities. The results of the flood impact analysis show that there is no net increase in base flood
elevations.
8c. What source(s) did you use to make the floodplain determination? FIRM Panel 4643 (Effective September 2, 2015); Flood
Risk Information System (FRIS)

Chris Tinklenberg, PWS

Applicant/Agent's Printed Name

_______________________________
Applicant/Agent's Signature
(Agent's signature is valid only if an authorization letter from the applicant
is provided.)

5/22/2020

Date

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WILLOW PONDPREPARED FORTOWN OF CORNELIUSCOVER SHEETC-1.0©Know what'sRDRAFTC-1.0COVER SHEETC-1.1GENERAL NOTESC-4.1 TO C-4.4PLAN AND PROFILEC-3.0 TO C-3.1TYPICAL SECTIONSC-5.0 TO C-5.2DETAILSC-1.2LEGEND AND SYMBOLSC-7.0VEGETATION NOTES AND DETAILSAPRIL 2020SCALE: 1" = 1200'VICINITY MAPENGINEER:OWNER:KIMLEY-HORN AND ASSOCIATES, INC.200 SOUTH TRYON STREETSUITE 200CHARLOTTE, NORTH CAROLINA 28202PHONE [phone]CONTACT: JAKE MASCHOFF, P.E.TOWN OF CORNELIUSPO BOX 399CORNELIUS, NC 28031PHONE [phone] EXT. 163CONTACT: TROY FITZSIMMONSSURVEYOR:CES GROUP ENGINEERS, LLP274 N HIGHWAY 16 BUSINESSSUITES 200-500DENVER, NC 28037PHONE [phone]CONTACT: JUDY HELEINEPHASE 1C-8.0 TO C-8.1EROSION CONTROL PLANC-9.0 TO C-9.1EROSION CONTROL NOTESC-10.0 TO C-10.4CROSS SECTIONSC-4.0OVERALL PLAN AND KEY SHEETC-7.1PLANTING PLANC-6.0 TO C-6.1GRADING PLANC-9.2 TO C-9.4EROSION CONTROL DETAILSC-2.0EXISTING CONDITIONS
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Photo Page 1

Photo 1 – Stream 2 (S2) – Perennial stream looking upstream, away from project boundary.

Photo 2 – Stream 2 (S2) – Perennial stream looking downstream.

Title Photo Pages
Prepared For
Project Upper McDowell Creek Tributary Stream Restoration
Cornelius, Mecklenburg County, North Carolina
Prepared By

Date Project Number
5/22/20 015598022

Photo Page 2

Photo 3 – Stream 2 (S2) – Perennial stream looking upstream.

Photo 4 – Stream 1 (S1) – Perennial stream looking upstream.

Title Photo Pages
Prepared For
Project Upper McDowell Creek Tributary Stream Restoration
Cornelius, Mecklenburg County, North Carolina
Prepared By

Date Project Number
5/22/20 015598022
Photo Page 3

Photo 5 – Stormwater collection area located on floodplain above S1.

Photo 6 –Stormwater drainage, looking up slope.

Title Photo Pages
Prepared For
Project Upper McDowell Creek Tributary Stream Restoration
Cornelius, Mecklenburg County, North Carolina
Prepared By

Date Project Number
5/22/20 015598022
Photo Page 4

Photo 7 –Stormwater drainage culvert originating offsite.

Photo 8 – Willow Pond spillway area.

Title Photo Pages
Prepared For
Project Upper McDowell Creek Tributary Stream Restoration
Cornelius, Mecklenburg County, North Carolina
Prepared By

Date Project Number
5/22/20 015598022

Photo Page 5

Photo 9 – Willow Pond, facing northwest.

Photo 10 – Stream 1 (S1) – Perennial stream looking upstream.

Title Photo Pages
Prepared For
Project Upper McDowell Creek Tributary Stream Restoration
Cornelius, Mecklenburg County, North Carolina
Prepared By

Date Project Number
5/22/20 015598022
Photo Page 6

Photo 11 – Stream 4 (S4) – Intermittent, rip-rap lined channel, looking upstream.

Photo 12 – Stream 3 (S3) – Perennial stream looking downstream.

Title Photo Pages
Prepared For
Project Upper McDowell Creek Tributary Stream Restoration
Cornelius, Mecklenburg County, North Carolina
Prepared By

Date Project Number
5/22/20 015598022

Photo Page 7

Photo 13 – Wetland 1 (W1) – Wetland area located near S3, facing downslope.

Photo 14 – Stream 3 (S3) – Perennial stream looking downstream.

Title Photo Pages
Prepared For
Project Upper McDowell Creek Tributary Stream Restoration
Cornelius, Mecklenburg County, North Carolina
Prepared By

Date Project Number
5/22/20 015598022

Photo Page 8

Photo 15 – Representative soil profile for W1-Wet.

Photo 16 – Representative soil profile for W1-Up.

Title Photo Pages
Prepared For
Project Upper McDowell Creek Tributary Stream Restoration
Cornelius, Mecklenburg County, North Carolina
Prepared By

Date Project Number
5/22/20 015598022

Jurisdictional Determination Request
Version: May 2017
Page 1

This form is intended for use by anyone requesting a jurisdictional determination (JD) from the
U.S. Army Corps of Engineers, Wilmington District (Corps). Please include all supporting
information, as described within each category, with your request. You may submit your request
via mail, electronic mail, or facsimile. Requests should be sent to the appropriate project
manager of the county in which the property is located. A current list of project managers by
assigned counties can be found on-line at:
http://www.saw.usace.army.mil/Missions/RegulatoryPermitProgram/Contact/CountyLocator.aspx,
by calling 910-251-4633, or by contacting any of the field offices listed below. Once your
request is received you will be contacted by a Corps project manager.
ASHEVILLE& CHARLOTTE REGULATORY
FIELDOFFICES
US ArmyCorps of Engineers
151 Patton Avenue, Room 208
Asheville, North Carolina28801-5006
GeneralNumber: [phone]
Fax Number: [phone]
RALEIGHREGULATORYFIELDOFFICE
US ArmyCorps of Engineers
3331 Heritage Trade Drive, Suite 105
Wake Forest, North Carolina27587
GeneralNumber: [phone]
Fax Number: [phone]
WASHINGTONREGULATORYFIELDOFFICE
US ArmyCorps of Engineers
2407 West Fifth Street
Washington, North Carolina27889
GeneralNumber: [phone]
Fax Number: [phone]
WILMINGTONREGULATORYFIELDOFFICE
US ArmyCorps of Engineers
69 Darlington Avenue
Wilmington, North Carolina 28403
GeneralNumber:910-251-4633
Fax Number: [phone]
INSTRUCTIONS:
All requestors must complete Parts A, B, C, D, E, F and G.
NOTE TO CONSULTANTS AND AGENCIES: If you are requesting a JD on behalf of a
paying client or your agency, please note the specific submittal requirements in Part H.
NOTE ON PART D – PROPERTY OWNER AUTHORIZATION: Please be aware that
all JD requests must include the current property owner authorization for the Corps to
proceed with the determination, which may include inspection of the property when
necessary. This form must be signed by the current property owner(s) or the owner(s)
authorized agent to be considered a complete request.
NOTE ON PART D - NCDOT REQUESTS: Property owner authorization/notification for
JD requests associated with North Carolina Department of Transportation (NCDOT)
projects will be conducted according to the current NCDOT/USACE protocols.
NOTE TO USDA PROGRAM PARTICIPANTS: A Corps approved or preliminary JD
may not be valid for the wetland conservation provisions of the Food Security Act of
1985. If you or your tenant are USDA Program participants, or anticipate participation in
USDA programs, you should also request a certified wetland determination from the local
office of the Natural Resources Conservation Service, prior to starting work.
Jurisdictional Determination Request
Version: May 2017
Page 2
A. PARCEL INFORMATION
Street Address: _______________________________________________
City, State: _______________________________________________
County:
Parcel Index Number(s) (PIN):
B. REQUESTORINFORMATION
Name:
Mailing Address:
_________________________________________
Telephone Number: _________________________________________
Electronic Mail Address: ________________________________________
Select one:
I am the current property owner.
I am an Authorized Agent or Environmental Consultant
1
Interested Buyer or Under Contract to Purchase
Other, please explain. ________________________________________
__________________________________________________________
C. PROPERTY OWNER INFORMATION
2
Name:
Mailing Address:
Telephone Number:
Electronic Mail Address:
_______________________________________________________________________________________________________________________
1 Must provide completed Agent Authorization Form/Letter.
2 Documentation of ownership also needs to be provided with request (copy of Deed, County GIS/Parcel/Tax Record).
Westmoreland Road to Catawba Avenue
Cornelius, North Carolina
Mecklenburg
N/A
Chris Tinklenberg, PWS
200 South Tryon Street, Suite 200
Charlotte, NC
[phone]
[e-mail]
Town of Cornelius (POC Tyler Beardsley)
P.O. Box 399
Cornelius, NC 28031
704.892.6031 ext. 127
[e-mail]
✔
Jurisdictional Determination Request
Version: May 2017
Page 3

D. PROPERTY ACCESS CERTIFICATION
3,4
By signing below, I authorize representatives of the Wilmington District, U.S. Army Corps of
Engineers (Corps) to enter upon the property herein described for the purpose of conducting on-
site investigations, if necessary, and issuing a jurisdictional determination pursuant to Section
404 of the Clean Water Act and/or Section 10 of the Rivers and Harbors Act of 1899. I, the
undersigned, am either a duly authorized owner of record of the property identified herein, or
acting as the duly authorized agent of the owner of record of the property.
Print Name
Capacity: Owner Authorized Agent5
Date
Signature
E. REASON FOR JD REQUEST:(Check as many as applicable)
I intend to construct/develop a project or perform activities on this parcel which would be
designed to avoid all aquatic resources.
I intend to construct/develop a project or perform activities on this parcel which would be
designed to avoid all jurisdictional aquatic resources underCorpsauthority.
Iintendto construct/develop a project or perform activities on this parcelwhich may
require authorization from the Corps, andthe JDwould beusedto avoid and minimize
impacts tojurisdictional aquatic resources and as aninitialstep in a future permitting
process.
I intendto construct/develop a project or perform activities on this parcelwhich may
require authorization from the Corps; this request is accompanied by my permit application
and the JD is to be used in the permitting process.
Iintendto construct/develop a project or perform activities in a navigable water of the
U.S. which is included on the district Section 10 list and/or is subject to the ebb and flow of
the tide.
A Corps JD is required in order obtain my local/state authorization.
I intend to contest jurisdiction over a particular aquatic resource and request the Corps
confirm that jurisdiction does/does not exist over the aquatic resource on the parcel.
I believe that the site may be comprised entirely of dry land.
Other:___________________________________________________________________
_______________________________________________________________________
3 For NCDOT requests following the current NCDOT/USACE protocols, skip to Part E.
4 If there are multiple parcels owned by different parties, please provide the following for each additional parcel on a
continuation sheet.
5 Must provide agent authorization form/letter signed by owner(s).
Chris Tinklenberg, PWS
5/22/2020
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Jurisdictional Determination Request
Version: May 2017
Page 4

F. JURISDICTIONAL DETERMINATION (JD) TYPE (Select One)
I am requesting that the Corps provide a preliminary JD for the property identified herein.
A Preliminary Jurisdictional Determination (PJD) provides an indication that there may
be “waters of the United States” or “navigable waters of the United States”on a property.
PJDs are sufficient as the basis for permit decisions. For the purposes of permitting, all
waters and wetlands on the property will be treated as if they are jurisdictional “waters of
the United States”. PJDs cannot be appealed (33 C.F.R. 331.2); however, a PJD is
“preliminary” in the sense that an approved JD can be requested at any time. PJDs do
not expire.
I am requesting that the Corps provide an approved JD for the property identified herein.
An Approved Jurisdictional Determination (AJD) is a determination that
jurisdictional “waters of the United States” or “navigable waters of the United
States” are either present or absent on a site. An approved JD identifies the limits of
waters on a site determined to be jurisdictional under the Clean Water Act and/or
Rivers and Harbors Act. Approved JDs are sufficient as the basis for permit
decisions. AJDs are appealable (33 C.F.R. 331.2). The results of the AJD will be
posted on the Corps website. A landowner, permit applicant, or other “affected
party” (33 C.F.R. 331.2) who receives an AJD may rely upon the AJD for five years
(subject to certain limited exceptions explained in Regulatory Guidance Letter 05-
02).
I am unclear as to which JD I would like to request and require additional information
to inform my decision.
G. ALL REQUESTS
Map of Property or Project Area. This Map must clearly depict the boundaries of the
review area.
Size of Property or Review Area acres.
The property boundary (or review area boundary) is clearly physically marked on the site.
64.6
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Jurisdictional Determination Request
Version: May 2017
Page 5

H. REQUESTS FROM CONSULTANTS
Project Coordinates (Decimal Degrees): Latitude: ______________________
Longitude: ______________________
A legible delineation map depicting the aquatic resources and the property/review area.
Delineation maps must be no larger than 11x17 and should contain the following: (Corps
signature of submitted survey plats will occur after the submitted delineation map has been
reviewed and approved).6
ƒNorth Arrow
ƒGraphical Scale
ƒBoundary of Review Area
ƒDate
ƒLocation of data points for each Wetland Determination Data Form or tributary
assessment reach.
For Approved Jurisdictional Determinations:
ƒJurisdictional wetland features should be labeled as Wetland Waters of the US, 404
wetlands, etc. Please include the acreage of these features.
ƒJurisdictional non-wetland features (i.e. tidal/navigable waters, tributaries,
impoundments) should be labeled as Non-Wetland Waters of the US, stream, tributary,
open water, relatively permanent water, pond, etc. Please include the acreage or linear
length of each of these features as appropriate.
ƒIsolated waters, waters that lack a significant nexus to navigable waters, or non-
jurisdictional upland features should be identified as Non-Jurisdictional. Please
include a justification in the label regarding why the feature is non-jurisdictional (i.e.
“Isolated”, “No Significant Nexus”, or “Upland Feature”). Please include the acreage
or linear length of these features as appropriate.
For Preliminary Jurisdictional Determinations:
ƒWetland and non-wetland features should not be identified as Jurisdictional, 404,
Waters of the United States, or anything that implies jurisdiction. These features can be
identified as Potential Waters of the United States, Potential Non-wetland Waters of
the United States, wetland, stream, open water, etc. Please include the acreage and
linear length of these features as appropriate.
Completed Wetland Determination Data Forms for appropriate region
(at least one wetland and one upland form needs to be completed for each wetland type)
____________________________________________________________________________
6 Please refer to the guidance document titled “Survey Standards for Jurisdictional Determinations” to ensure that the
supplied map meets the necessary mapping standards.http://www.saw.usace.army.mil/Missions/Regulatory-Permit-
Program/Jurisdiction/
35.470624 N
-80.871835 W
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Jurisdictional Determination Request
Version: May 2017
Page 6

Completed appropriate Jurisdictional Determination form
x PJDs,please complete a Preliminary Jurisdictional Determination Form7 and include the
Aquatic Resource Table
x AJDs, please complete an Approved Jurisdictional Determination Form
8
Vicinity Map
Aerial Photograph
USGS Topographic Map
Soil Survey Map
Other Maps, as appropriate (e.g. National Wetland Inventory Map, Proposed Site
Plan, previous delineation maps, LIDAR maps, FEMA floodplain maps)
Landscape Photos (if taken)
NCSAM and/or NCWAM Assessment Forms and Rating Sheets
NC Division of Water Resources Stream Identification Forms
Other Assessment Forms
_____________________________________________________________________________
7 www.saw.usace.army.mil/Portals/59/docs/regulatory/regdocs/JD/RGL_08-02_App_A_Prelim_JD_Form_fillable.pdf
8 Please see http://www.saw.usace.army.mil/Missions/Regulatory-Permit-Program/Jurisdiction/
Principal Purpose:The information thatyouprovide will beusedinevaluating your requestto determine
whether thereareany aquatic resources within the project areasubjecttofederaljurisdictionunder the regulatory
authorities referencedabove.
RoutineUses:Thisinformation maybeshared with the Departmentof Justice andotherfederal, state,and local
government agencies, and the public,andmaybe made available aspartof a public notice as required byfederal
law. Your nameandproperty location wherefederal jurisdiction is to bedetermined will beincluded in the
approved jurisdictional determination (AJD),which will bemade available tothe public on the District's website
andontheHeadquartersUSAGEwebsite.
Disclosure:Submission ofrequested information is voluntary; however, ifinformation is notprovided, the
requestforanAJDcannot beevaluatednorcananAJD be issued.
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Appendix 2 - PRELIMINARY JURISDICTIONAL DETERMINATION (PJD) FORM
BACKGROUND INFORMATION
A.REPORT COMPLETION DATE FOR PJD:
B.NAME AND ADDRESS OF PERSON REQUESTING PJD:
C.DISTRICT OFFICE, FILE NAME, AND NUMBER:
D.PROJECT LOCATION(S) AND BACKGROUND INFORMATION:
(USE THE TABLE BELOW TO DOCUMENT MULTIPLE AQUATIC RESOURCES AND/OR
AQUATIC RESOURCES AT DIFFERENT SITES)
State: County/parish/borough: City:
Center coordinates of site (lat/long in degree decimal format):
Lat.:Long.:
Universal Transverse Mercator:
Name of nearest waterbody:
E.REVIEW PERFORMED FOR SITE EVALUATION (CHECK ALL THAT APPLY):
Office (Desk) Determination. Date:
Field Determination. Date(s):
TABLE OF AQUATIC RESOURCES IN REVIEW AREA WHICH “MAY BE”SUBJECT TO REGULATORY
JURISDICTION.
Site
number
Latitude
(decimal
degrees)
Longitude
(decimal
degrees)
Estimated amount
of aquatic resource
in review area
(acreage and linear
feet, if applicable)
Type of aquatic
resource (i.e., wetland
vs. non-wetland
waters)
Geographic authority
to which the aquatic
resource “may be”
subject (i.e., Section
404 or Section 10/404)
S1 35.471047 -80.872308 2,316 lf
non-wetland waters Section 404
S2 35.472613 -80.872834 696 lf
non-wetland waters Section 404
S3 35.476637 -80.872834 1,296 lf non-wetland waters Section 404
S4 35.470403 -80.870084 225 non-wetland waters Section 404
W1 35.469799 -80.869724 0.24 ac
wetland waters Section 404
OW1 35.474367 -80.872717 1.6 ac
non-wetland waters Section 404
Chris Tinklenberg, 200 S. Tryon St., Ste 200, Charlotte, NC 28202
NC Mecklenburg Cornelius
35.470624 N -80.871835 W
17N
McDowell Creek
1) The Corps of Engineers believes that there may be jurisdictional aquatic resources in
the review area, and the requestor of this PJD is hereby advised of his or her option
to request and obtain an approved JD (AJD) for that review area based on an
informed decision after having discussed the various types of JDs and their
characteristics and circumstances when they may be appropriate.
2) In any circumstance where a permit applicant obtains an individual permit, or a
Nationwide General Permit (NWP) or other general permit verification requiring “pre-
construction notification” (PCN), or requests verification for a non-reporting NWP or
other general permit, and the permit applicant has not requested an AJD for the
activity, the permit applicant is hereby made aware that: (1) the permit applicant has
elected to seek a permit authorization based on a PJD, which does not make an
official determination of jurisdictional aquatic resources; (2) the applicant has the
option to request an AJD before accepting the terms and conditions of the permit
authorization, and that basing a permit authorization on an AJD could possibly result
in less compensatory mitigation being required or different special conditions; (3) the
applicant has the right to request an individual permit rather than accepting the terms
and conditions of the NWP or other general permit authorization; (4) the applicant can
accept a permit authorization and thereby agree to comply with all the terms and
conditions of that permit, including whatever mitigation requirements the Corps has
determined to be necessary; (5) undertaking any activity in reliance upon the subject
permit authorization without requesting an AJD constitutes the applicant’s acceptance
of the use of the PJD; (6) accepting a permit authorization (e.g., signing a proffered
individual permit)or undertaking any activity in reliance on any form of Corps permit
authorization based on a PJD constitutes agreement that all aquatic resources in the
review area affected in any way by that activity will be treated as jurisdictional, and
waives any challenge to such jurisdiction in any administrative or judicial compliance
or enforcement action, or in any administrative appeal or in any Federal court; and (7)
whether the applicant elects to use either an AJD or a PJD, the JD will be processed
as soon as practicable. Further, an AJD, a proffered individual permit (and all terms
and conditions contained therein), or individual permit denial can be administratively
appealed pursuant to 33 C.F.R. Part 331. If, during an administrative appeal, it
becomes appropriate to make an official determination whether geographic
jurisdiction exists over aquatic resources in the review area, or to provide an official
delineation of jurisdictional aquatic resources in the review area, the Corps will
provide an AJD to accomplish that result, as soon as is practicable. This PJD finds
that there “may be” waters of the U.S. and/or that there “may be”navigable waters of
the U.S. on the subject review area, and identifies all aquatic features in the review
area that could be affected by the proposed activity, based on the following
information:
SUPPORTING DATA. Data reviewed for PJD (check all that apply)
Checked items should be included in subject file. Appropriately reference sources
below where indicated for all checked items:
Maps, plans, plots or plat submitted by or on behalf of the PJD requestor:
Map: ________________BBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBB.
Data sheets prepared/submitted by or on behalf of the PJD requestor.
Office concurs with data sheets/delineation report.
Office does not concur with data sheets/delineation report. Rationale: _______BBBBBBBBBBBB.
Data sheets prepared by the Corps: ________BBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBB.
Corps navigable waters’ study: ____________BBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBB.
U.S. Geological Survey Hydrologic Atlas: ________BBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBB.
USGS NHD data.
USGS 8 and 12 digit HUC maps.
U.S. Geological Survey map(s). Cite scale & quad name: _________BBBBBBBBBBBBBBBBBBBBBB.
Natural Resources Conservation Service Soil Survey. Citation: __________BBBBBBBBBBBBBBBBB.
National wetlands inventory map(s). Cite name: ________BBBBBBBBBBBBBBBBBBBBBBBBBBBBBB.
State/local wetland inventory map(s): ____________BBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBB.
FEMA/FIRM maps: ________________BBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBB.
100-year Floodplain Elevation is: ____BBBBBBBBBBBB.(National Geodetic Vertical Datum of 1929)
Photographs: Aerial (Name & Date): ______BBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBB.
or Other (Name & Date): ______BBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBB.
Previous determination(s). File no. and date of response letter: __________BBBBBBBBBBBBBBBB.
Other information (please specify): ______________BBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBBB.
IMPORTANT NOTE: The information recorded on this form has not necessarily
been verified by the Corps and should not be relied upon for later jurisdictional
determinations.
Signature and date of Signature and date of
Regulatory staff member person requesting PJD
completing PJD (REQUIRED, unless obtaining
the signature is impracticable)
1
1 Districts may establish timeframes for requestor to return signed PJD forms. If the requestor does not respond
within the established time frame, the district may presume concurrence and no additional follow up is
necessary prior to finalizing an action.
1:24K - Lake Norman South, Cornelius
Meck. Co. SSURGO Soils
NWI digital data
2019 Meck. County Aerial
Site photographs July, 2018
Date: Project/Site: Latitude:
Evaluator: County: Longitude:
Total Points:34
Stream is at least intermittent
if ≥ 19 or perennial if ≥ 30
A. Geomorphology Subtotal = Absent Weak Strong Score
0 1 3 3
0 1 3 2
0 1 3 2
0 1 3 2
0 1 3 3
0 1 3 3
0 1 3 2
0 1 3 1
0 0.5 1.5 0
0 0.5 1.5 1
0
a artificial ditches are not rated; see discussions in manual
B. Hydrology Subtotal = 9
0 1 3 3
0 1 3 0
1.5 1 0 1
0 0.5 1.5 1
0 0.5 1.5 1
3
C. Biology Subtotal = 6
3 2 0 3
3 2 0 3
0 1 3 0
0 1 3 0
0 0.5 1.5 0
0 0.5 1.5 0
0 0.5 1.5 0
0 0.5 1.5 0
0
*perennial streams may also be identified using other methods. See p. 35 of manual.
Notes:
Well defined channel and strong baseflow throughout reach
Incised banks
1a. Continuity of channel bed and bank 2
North Carolina Division of Water Quality - Stream Identification Form, Version 4.11
10/24/2018 Stream 1 35.471047
Chris Tinklenberg & Addie
Lasitter Mecklenburg -80.872308
Stream Determination (circle one)
Ephemeral Intermittent Perennial
Other
e.g. Quad Name:
Lake Norman
South; Cornelius
19 Moderate
2. Sinuosity of channel along thalweg 2
3. In-channel structure: ex. riffle-pool, step-pool, ripple-
pool sequence 2
4. Particle size of stream substrate 2
5. Active/relic floodplain 2
6. Depositional bars or benches 2
7. Recent alluvial deposits 2
13. Iron oxidizing bacteria 2
8. Headcuts 2
9. Grade control 1
10. Natural valley 1
11. Second or greater order channel No = 0 Yes = 3
12. Presence of Baseflow 2
19. Rooted upland plants in streambed 1
14. Leaf litter 0.5
15. Sediment on plants or debris 1
16. Organic debris lines or piles 1
17. Soil-based evidence of high water table?No = 0 Yes = 3
18. Fibrous roots in streambed 1
20. Macrobenthos (note diversity and abundance)2
21. Aquatic Mollusks 2
22. Fish 1
26. Wetland plants in streambed FACW = 0.75; OBL = 1.5; Other = 0
23. Crayfish 1
24. Amphibians 1
25. Algae 1
Date: Project/Site: Latitude:
Evaluator: County: Longitude:
Total Points:41.5
Stream is at least intermittent
if ≥ 19 or perennial if ≥ 30
A. Geomorphology Subtotal = Absent Weak Strong Score
0 1 3 3
0 1 3 3
0 1 3 3
0 1 3 2
0 1 3 2
0 1 3 3
0 1 3 3
0 1 3 0
0 0.5 1.5 1
0 0.5 1.5 1
3
a artificial ditches are not rated; see discussions in manual
B. Hydrology Subtotal = 11
0 1 3 3
0 1 3 1
1.5 1 0 1.5
0 0.5 1.5 1
0 0.5 1.5 1.5
3
C. Biology Subtotal = 6.5
3 2 0 3
3 2 0 3
0 1 3 0
0 1 3 0
0 0.5 1.5 0.5
0 0.5 1.5 0
0 0.5 1.5 0
0 0.5 1.5 0
0
*perennial streams may also be identified using other methods. See p. 35 of manual.
Notes:
Well defined channel and strong baseflow throughout reach
Incised bank throughout reach
26. Wetland plants in streambed FACW = 0.75; OBL = 1.5; Other = 0
23. Crayfish 1
24. Amphibians 1
25. Algae 1
20. Macrobenthos (note diversity and abundance)2
21. Aquatic Mollusks 2
22. Fish 1
19. Rooted upland plants in streambed 1
14. Leaf litter 0.5
15. Sediment on plants or debris 1
16. Organic debris lines or piles 1
17. Soil-based evidence of high water table?No = 0 Yes = 3
18. Fibrous roots in streambed 1
13. Iron oxidizing bacteria 2
8. Headcuts 2
9. Grade control 1
10. Natural valley 1
11. Second or greater order channel No = 0 Yes = 3
12. Presence of Baseflow 2
5. Active/relic floodplain 2
6. Depositional bars or benches 2
7. Recent alluvial deposits 2
2. Sinuosity of channel along thalweg 2
3. In-channel structure: ex. riffle-pool, step-pool, ripple-
pool sequence 2
4. Particle size of stream substrate 2
1a. Continuity of channel bed and bank 2
North Carolina Division of Water Quality - Stream Identification Form, Version 4.11
10/24/2018 McDowell Creek - Stream
S2 35.472613
Chris Tinklenberg & Addie
Lasitter Mecklenburg -80.872834
Stream Determination (circle one)
Ephemeral Intermittent Perennial
Other
e.g. Quad Name:
Lake Norman
South; Cornelius
24 Moderate
Date: Project/Site: Latitude:
Evaluator: County: Longitude:
Total Points:34
Stream is at least intermittent
if ≥ 19 or perennial if ≥ 30
A. Geomorphology Subtotal = Absent Weak Strong Score
0 1 3 3
0 1 3 2
0 1 3 1
0 1 3 1
0 1 3 2
0 1 3 3
0 1 3 2
0 1 3 0
0 0.5 1.5 1
0 0.5 1.5 1
3
a artificial ditches are not rated; see discussions in manual
B. Hydrology Subtotal = 9
0 1 3 3
0 1 3 0
1.5 1 0 1
0 0.5 1.5 1
0 0.5 1.5 1
3
C. Biology Subtotal = 6
3 2 0 3
3 2 0 3
0 1 3 0
0 1 3 0
0 0.5 1.5 0
0 0.5 1.5 0
0 0.5 1.5 0
0 0.5 1.5 0
0
*perennial streams may also be identified using other methods. See p. 35 of manual.
Notes:
Well defined channel and strong baseflow throughout reach
26. Wetland plants in streambed FACW = 0.75; OBL = 1.5; Other = 0
23. Crayfish 1
24. Amphibians 1
25. Algae 1
20. Macrobenthos (note diversity and abundance)2
21. Aquatic Mollusks 2
22. Fish 1
19. Rooted upland plants in streambed 1
14. Leaf litter 0.5
15. Sediment on plants or debris 1
16. Organic debris lines or piles 1
17. Soil-based evidence of high water table?No = 0 Yes = 3
18. Fibrous roots in streambed 1
13. Iron oxidizing bacteria 2
8. Headcuts 2
9. Grade control 1
10. Natural valley 1
11. Second or greater order channel No = 0 Yes = 3
12. Presence of Baseflow 2
5. Active/relic floodplain 2
6. Depositional bars or benches 2
7. Recent alluvial deposits 2
2. Sinuosity of channel along thalweg 2
3. In-channel structure: ex. riffle-pool, step-pool, ripple-
pool sequence 2
4. Particle size of stream substrate 2
1a. Continuity of channel bed and bank 2
North Carolina Division of Water Quality - Stream Identification Form, Version 4.11
10/24/2018 Stream 3 35.470403
Chris Tinklenberg & Addie
Lasitter Mecklenburg -80.870084
Stream Determination (circle one)
Ephemeral Intermittent Perennial
Other
e.g. Quad Name:
Lake Norman
South; Cornelius
19 Moderate
Date: Project/Site: Latitude:
Evaluator: County: Longitude:
Total Points:21
Stream is at least intermittent
if ≥ 19 or perennial if ≥ 30
A. Geomorphology Subtotal = Absent Weak Strong Score
0 1 3 2
0 1 3 1
0 1 3 1
0 1 3 3
0 1 3 0
0 1 3 0
0 1 3 0
0 1 3 0
0 0.5 1.5 0.5
0 0.5 1.5 0.5
0
a artificial ditches are not rated; see discussions in manual
B. Hydrology Subtotal = 7
0 1 3 2
0 1 3 0
1.5 1 0 1
0 0.5 1.5 0
0 0.5 1.5 1
3
C. Biology Subtotal = 6
3 2 0 3
3 2 0 3
0 1 3 0
0 1 3 0
0 0.5 1.5 0
0 0.5 1.5 0
0 0.5 1.5 0
0 0.5 1.5 0
0
*perennial streams may also be identified using other methods. See p. 35 of manual.
Notes:
Minimal flow observed at upstream reach
Likely influenced mostly by storm-flow from neighborhood
Rip-rap lined channel
Incised banks
26. Wetland plants in streambed FACW = 0.75; OBL = 1.5; Other = 0
23. Crayfish 1
24. Amphibians 1
25. Algae 1
20. Macrobenthos (note diversity and abundance)2
21. Aquatic Mollusks 2
22. Fish 1
19. Rooted upland plants in streambed 1
14. Leaf litter 0.5
15. Sediment on plants or debris 1
16. Organic debris lines or piles 1
17. Soil-based evidence of high water table?No = 0 Yes = 3
18. Fibrous roots in streambed 1
13. Iron oxidizing bacteria 2
8. Headcuts 2
9. Grade control 1
10. Natural valley 1
11. Second or greater order channel No = 0 Yes = 3
12. Presence of Baseflow 2
5. Active/relic floodplain 2
6. Depositional bars or benches 2
7. Recent alluvial deposits 2
2. Sinuosity of channel along thalweg 2
3. In-channel structure: ex. riffle-pool, step-pool, ripple-
pool sequence 2
4. Particle size of stream substrate 2
1a. Continuity of channel bed and bank 2
North Carolina Division of Water Quality - Stream Identification Form, Version 4.11
10/24/2018 Stream 4 35.251821
Chris Tinklenberg & Addie
Lasitter Mecklenburg -80.881138
Stream Determination (circle one)
Ephemeral Intermittent Perennial
Other
e.g. Quad Name:
Lake Norman
South; Cornelius
8 Moderate
USACE AID #:NCDWR #:
PROJECT / SITE INFORMATION:
1. Project name (if any):2. Date of evaluation:
3. Applicant/owner name:
5. County:6. Nearest named water body
7. River Basin: on USGS 7.5-minute quad:
8. Site coordinates (decimal degrees, at lower end of assessment reach):
STREAM INFORMATION: (depth and width can be approximations)
9. Site number (show on attached map):10. Length of assessment reach evaluated (feet):
11. Channel depth from bed (in riffle, if present) to top of bank (feet):Unable to assess channel depth.
12. Channel width at top of bank (feet):13. Is assessment reach a swamp stream?Yes No
14. Feature type:Perennial flow Intermittent flow Tidal Marsh Stream
STREAM RATING INFORMATION:
15. NC SAM Zone:Mountains (M)Piedmont (P)Inner Coastal Plain (I)Outer Coastal Plain (O)
16. Estimated geomorphic
valley shape (skip for a b
Tidal Marsh Stream):(more sinuous stream, flatter valley slope)(less sinuous stream, steeper valley slope)
17. Watershed size: (skip Size 1 (< 0.1 mi2)Size 2 (0.1 to < 0.5 mi2)Size 3 (0.5 to < 5 mi2)Size 4 (≥ 5 mi2)
for Tidal Marsh Stream)
ADDITIONAL INFORMATION:
18. Were regulatory considerations evaluated?Yes No If Yes, check all that appy to the assessment area.
Section 10 water Classified Trout Waters Water Supply Watershed (I II III IV V)
Essential Fish Habitat Primary Nursery Area High Quality Waters/Outstanding Resource Waters
Publicly owned property NCDWR riparian buffer rule in effect Nutrient Sensitive Waters
Anadromous fish 303(d) List CAMA Area of Environmental Concern (AEC)
Documented presence of a federal and/or state listed protected species within the assessment area.
List species:
Designated Critical Habitat (list species):
19. Are additional stream information/supplementary measurements included in "Notes/Sketch" section or attached?Yes No
1.Channel Water – assessment reach metric (skip for Size 1 streams and Tidal Marsh Streams)
A Water throughout assessment reach.
B No flow, water in pools only.
C No water in assessment reach.
2.Evidence of Flow Restriction – assessment reach metric
A At least 10% of assessment reach in-stream habitat or riffle-pool sequence is adversely affected by a flow restriction or fill to the
point of obstructing flow or a channel choked with aquatic macrophytes or ponded water or impounded on flood or ebb within
the assessment reach (examples: undersized or perched culverts, causeways that constrict the channel, tidal gates).
B Not A
3.Feature Pattern – assessment reach metric
A A majority of the assessment reach has altered pattern (examples: straightening, modification above or below culvert).
B Not A.
4.Feature Longitudinal Profile – assessment reach metric
A Majority of assessment reach has a substantially altered stream profile (examples: channel down-cutting, existing damming,
over widening, active aggradation, dredging, and excavation where appropriate channel profile has not reformed from any of
these disturbances).
B Not A
5.Signs of Active Instability – assessment reach metric
Consider only current instability, not past events from which the stream has currently recovered. Examples of instability include
active bank failure, active channel down-cutting (head-cut), active widening, and artificial hardening (such as concrete, gabion, rip-rap).
A < 10% of channel unstable
B 10 to 25% of channel unstable
C > 25% of channel unstable
6.Streamside Area Interaction – streamside area metric
Consider for the Left Bank (LB) and the Right Bank (RB).
LB RB
A A Little or no evidence of conditions that adversely affect reference interaction
B B Moderate evidence of conditions (examples: berms, levees, down-cutting, aggradation, dredging) that adversely affect
reference interaction (examples: limited streamside area access, disruption of flood flows through streamside area,
leaky or intermittent bulkheads, causeways with floodplain constriction, minor ditching [including mosquito ditching])
C C Extensive evidence of conditions that adversely affect reference interaction (little to no floodplain/intertidal zone access
[examples: causeways with floodplain and channel constriction, bulkheads, retaining walls, fill, stream incision,
disruption of flood flows through streamside area] or too much floodplain/intertidal zone access [examples:
impoundments, intensive mosquito ditching]) or floodplain/intertidal zone unnaturally absent or assessment reach is a
man-made feature on an interstream divide
7.Water Quality Stressors – assessment reach/intertidal zone metric
Check all that apply.
A Discolored water in stream or intertidal zone (milky white, blue, unnatural water discoloration, oil sheen, stream foam)
B Excessive sedimentation (burying of stream features or intertidal zone)
Willow Greenway and Upper McDowell Creek Restoration 10/24/18
35.471047, -80.872308
Stream 1 ~150
Town of Cornelius 4. Assessor name/organization:Addie Lasitter / Kimley-Horn
Mecklenburg
Catawba McDowell Creek
Manual for detailed descriptions and explanations of requested information. Record in the "Notes/Sketch" section if any supplementary
NOTE EVIDENCE OF STRESSORS AFFECTING THE ASSESSMENT AREA (do not need to be within the assessment area).
measurements were performed. See the NC SAM User Manual for examples of additional measurements that may be relevant.
NC SAM FIELD ASSESSMENT FORM
Accompanies User Manual Version 2.1
INSTRUCTIONS:Attach a sketch of the assessment area and photographs.Attach a copy of the USGS 7.5-minute topographic
quadrangle,and circle the location of the stream reach under evaluation.If multiple stream reaches will be evaluated on the same
property,identify and number all reaches on the attached map,and include a separate form for each reach.See the NC SAM User
4
10
C Noticeable evidence of pollutant discharges entering the assessment reach and causing a water quality problem
D Odor (not including natural sulfide odors)
E Current published or collected data indicating degraded water quality in the assessment reach. Cite source in the "Notes/Sketch"
section.
F Livestock with access to stream or intertidal zone
G Excessive algae in stream or intertidal zone
H Degraded marsh vegetation in the intertidal zone (removal, burning, regular mowing, destruction, etc.)
I Other:(explain in "Notes/Sketch" section)
J Little to no stressors
8.Recent Weather – watershed metric
For Size 1 or 2 streams, D1 drought or higher is considered a drought; for Size 3 or 4 streams, D2 drought or higher is considered a
drought.
A Drought conditions and no rainfall or rainfall not exceeding 1 inch within the last 48 hours
B Drought conditions and rainfall exceeding 1 inch within the last 48 hours
C No drought conditions
9 Large or Dangerous Stream – assessment reach metric
Yes No Is stream is too large or dangerous to assess? If Yes, skip to Metric 13 (Streamside Area Ground Surface Condition).
10.Natural In-stream Habitat Types – assessment reach metric
10a.Yes No Degraded in-stream habitat over majority of the assessment reach (examples of stressors include excessive
sedimentation, mining, excavation, in-stream hardening [for example, rip-rap], recent dredging, and snagging)
(evaluate for size 4 Coastal Plain streams only, then skip to Metric 12)
10b.Check all that occur (occurs if > 5% coverage of assessment reach) (skip for Size 4 Coastal Plain streams)
A Multiple aquatic macrophytes and aquatic mosses F 5% oysters or other natural hard bottoms
(include liverworts, lichens, and algal mats)G Submerged aquatic vegetation
B Multiple sticks and/or leaf packs and/or emergent H Low-tide refugia (pools)
vegetation I Sand bottom
C Multiple snags and logs (including lap trees)J 5% vertical bank along the marsh
D 5% undercut banks and/or root mats and/or roots K Little or no habitat
in banks extend to the normal wetted perimeter
E Little or no habitat
11.Bedform and Substrate – assessment reach metric (skip for Size 4 Coastal Plain streams and Tidal Marsh Streams)
11a.Yes No Is assessment reach in a natural sand-bed stream? (skip for Coastal Plain streams)
11b.Bedform evaluated. Check the appropriate box(es).
A Riffle-run section (evaluate 11c)
B Pool-glide section (evaluate 11d)
C Natural bedform absent (skip to Metric 12, Aquatic Life)
11c.In riffles sections, check all that occur below the normal wetted perimeter of the assessment reach – whether or not submerged.
Check at least one box in each row (skip for Size 4 Coastal Plain Streams and Tidal Marsh Streams). Not Present (NP) =
absent, Rare (R) = present but ≤ 10%, Common (C) = > 10-40%, Abundant (A) = > 40-70%, Predominant (P) = > 70%. Cumulative
percentages should not exceed 100% for each assessment reach.
NP R C A P
Bedrock/saprolite
Boulder (256 – 4096 mm)
Cobble (64 – 256 mm)
Gravel (2 – 64 mm)
Sand (.062 – 2 mm)
Silt/clay (< 0.062 mm)
Detritus
Artificial (rip-rap, concrete, etc.)
11d.Yes No Are pools filled with sediment? (skip for Size 4 Coastal Plain streams and Tidal Marsh Streams)
12.Aquatic Life – assessment reach metric (skip for Size 4 Coastal Plain streams and Tidal Marsh Streams)
12a.Yes No Was an in-stream aquatic life assessment performed as described in the User Manual?
If No, select one of the following reasons and skip to Metric 13. No Water Other:
12b.Yes No Are aquatic organisms present in the assessment reach (look in riffles, pools, then snags)? If Yes, check
all that apply. If No, skip to Metric 13.
1 >1 Numbers over columns refer to “individuals” for size 1 and 2 streams and “taxa” for size 3 and 4 streams.
Adult frogs
Aquatic reptiles
Aquatic macrophytes and aquatic mosses (include liverworts, lichens, and algal mats)
Beetles (including water pennies)
Caddisfly larvae (Trichoptera [T])
Asian clam (Corbicula )
Crustacean (isopod/amphipod/crayfish/shrimp)
Damselfly and dragonfly larvae
Dipterans (true flies)
Mayfly larvae (Ephemeroptera [E])
Megaloptera (alderfly, fishfly, dobsonfly larvae)
Midges/mosquito larvae
Mosquito fish (Gambusia ) or mud minnows (Umbra pygmaea)
Mussels/Clams (not Corbicula )
Other fish
Salamanders/tadpoles
Snails
Stonefly larvae (Plecoptera [P])
Tipulid larvae
*********************************REMAINING QUESTIONS ARE NOT APPLICABLE FOR TIDAL MARSH STREAMS****************************Check for TidalMarsh Streamsonly
Worms/leeches
13.Streamside Area Ground Surface Condition – streamside area metric (skip for Tidal Marsh Streams and B valley types)
Consider for the Left Bank (LB) and the Right Bank (RB). Consider storage capacity with regard to both overbank flow and
upland runoff.
LB RB
A A Little or no alteration to water storage capacity over a majority of the streamside area
B B Moderate alteration to water storage capacity over a majority of the streamside area
C C Severe alteration to water storage capacity over a majority of the streamside area (examples include: ditches, fill,
soil, compaction, livestock disturbance, buildings, man-made levees, drainage pipes)
14.Streamside Area Water Storage – streamside area metric (skip for Size 1 streams, Tidal Marsh Streams, and B valley types)
Consider for the Left Bank (LB) and the Right Bank (RB) of the streamside area.
LB RB
A A Majority of streamside area with depressions able to pond water ≥ 6 inches deep
B B Majority of streamside area with depressions able to pond water 3 to 6 inches deep
C C Majority of streamside area with depressions able to pond water < 3 inches deep
15.Wetland Presence – streamside area metric (skip for Tidal Marsh Streams)
Consider for the Left Bank (LB) and the Right Bank (RB). Do not consider wetlands outside of the streamside area or within the
normal wetted perimeter of assessment reach.
LB RB
Y Y Are wetlands present in the streamside area?
N N
16.Baseflow Contributors – assessment reach metric (skip for size 4 streams and Tidal Marsh Streams)
Check all contributors within the assessment reach or within view of and draining to the assessment reach.
A Streams and/or springs (jurisdictional discharges)
B Ponds (include wet detention basins; do not include sediment basins or dry detention basins)
C Obstruction that passes some flow during low-flow periods within assessment area (beaver dam, bottom-release dam)
D Evidence of bank seepage or sweating (iron oxidizing bacteria in water indicates seepage)
E Stream bed or bank soil reduced (dig through deposited sediment if present)
F None of the above
17.Baseflow Detractors – assessment area metric (skip for Tidal Marsh Streams)
Check all that apply.
A Evidence of substantial water withdrawals from the assessment reach (includes areas excavated for pump installation)
B Obstruction not passing flow during low flow periods affecting the assessment reach (ex: watertight dam, sediment deposit)
C Urban stream (≥ 24% impervious surface for watershed)
D Evidence that the stream-side area has been modified resulting in accelerated drainage into the assessment reach
E Assessment reach relocated to valley edge
F None of the above
18.Shading – assessment reach metric (skip for Tidal Marsh Streams)
Consider aspect. Consider “leaf-on” condition.
A Stream shading is appropriate for stream category (may include gaps associated with natural processes)
B Degraded (example: scattered trees)
C Stream shading is gone or largely absent
19.Buffer Width – streamside area metric (skip for Tidal Marsh Streams)
Consider “vegetated buffer” and “wooded buffer” separately for left bank (LB) and right bank (RB) starting at the top
of bank out to the first break.
Vegetated Wooded
LB RB LB RB
A A A A ≥ 100-feet wide or extends to the edge of the watershed
B B B B From 50 to < 100-feet wide
C C C C From 30 to < 50-feet wide
D D D D From 10 to < 30-feet wide
E E E E < 10-feet wide or no trees
20.Buffer Structure – streamside area metric (skip for Tidal Marsh Streams)
Consider for left bank (LB) and right bank (RB) for Metric 19 ("Vegetated" Buffer Width).
LB RB
A A Mature forest
B B Non-mature woody vegetation or modified vegetation structure
C C Herbaceous vegetation with or without a strip of trees < 10 feet wide
D D Maintained shrubs
E E Little or no vegetation
21.Buffer Stressors – streamside area metric (skip for Tidal Marsh Streams)
Check all appropriate boxes for left bank (LB) and right bank (RB). Indicate if listed stressor abuts stream (Abuts), does not abut but
is within 30 feet of stream (< 30 feet), or is between 30 to 50 feet of stream (30-50 feet).
If none of the following stressors occurs on either bank, check here and skip to Metric 22:
Abuts < 30 feet 30-50 feet
LB RB LB RB LB RB
A A A A A A Row crops
B B B B B B Maintained turf
C C C C C C Pasture (no livestock)/commercial horticulture
D D D D D D Pasture (active livestock use)
22.Stem Density – streamside area metric (skip for Tidal Marsh Streams)
Consider for left bank (LB) and right bank (RB) for Metric 19 ("Wooded" Buffer Width).
LB RB
A A Medium to high stem density
B B Low stem density
C C No wooded riparian buffer or predominantly herbaceous species or bare ground
23.Continuity of Vegetated Buffer – streamside area metric (skip for Tidal Marsh Streams)
Consider whether vegetated buffer is continuous along stream (parallel). Breaks are areas lacking vegetation > 10-feet wide.
LB RB
A A The total length of buffer breaks is < 25 percent.
B B The total length of buffer breaks is between 25 and 50 percent.
C C The total length of buffer breaks is > 50 percent.
24.Vegetative Composition – First 100 feet of streamside area metric (skip for Tidal Marsh Streams)
Evaluate the dominant vegetation within 100 feet of each bank or to the edge of the watershed (whichever comes first) as it contributes
to assessment reach habitat.
LB RB
A A Vegetation is close to undisturbed in species present and their proportions. Lower strata composed of native
species, with non-native invasive species absent or sparse.
B B Vegetation indicates disturbance in terms of species diversity or proportions, but is still largely composed of native
species. This may include communities of weedy native species that develop after clear-cutting or clearing or
communities with non-native invasive species present, but not dominant, over a large portion of the expected strata or
communities missing understory but retaining canopy trees.
C C Vegetation is severely disturbed in terms of species diversity or proportions. Mature canopy is absent or communities
with non-native invasive species dominant over a large portion of expected strata or communities composed of planted
stands of non-characteristic species or communities inappropriately composed of a single species or no vegetation.
25.Conductivity – assessment reach metric (skip for all Coastal Plain streams)
25a.Yes No Was a conductivity measurement recorded?
If No, select one of the following reasons. No Water Other:
25b.Check the box corresponding to the conductivity measurement (units of microsiemens per centimeter).
A <46 B 46 to < 67 C 67 to < 79 D 79 to < 230 E ≥ 230
Notes/Sketch:
Notes of Field Assessment Form (Y/N)
Presence of regulatory considerations (Y/N)
Additional stream information/supplementary measurements included (Y/N)
NC SAM feature type (perennial, intermittent, Tidal Marsh Stream)
(4) Floodplain Access
(4) Wooded Riparian Buffer
(4) Microtopography
(3) Stream Stability
(4) Channel Stability
(4) Sediment Transport
(4) Stream Geomorphology
(2) Stream/Intertidal Zone Interaction
(2) Longitudinal Tidal Flow
(2) Tidal Marsh Stream Stability
(3) Tidal Marsh Stream Geomorphology
(1) Water Quality
(2) Baseflow
(2) Streamside Area Vegetation
(3) Upland Pollutant Filtration
(3) Thermoregulation
(2) Indicators of Stressors
(2) Aquatic Life Tolerance
(2) Intertidal Zone Filtration
(1) Habitat
(2) In-stream Habitat
(3) Baseflow
(3) Substrate
(3) Stream Stability
(3) In-stream Habitat
(2) Stream-side Habitat
(3) Stream-side Habitat
(3) Thermoregulation
(2) Tidal Marsh In-stream Habitat
(3) Flow Restriction
(3) Tidal Marsh Stream Stability
(4) Tidal Marsh Stream Geomorphology
(3) Tidal Marsh In-stream Habitat
(2) Intertidal Zone Habitat
Overall LOW
LOW
HIGH
LOW
MEDIUM
LOW
HIGH
NA
NA
MEDIUM
NA
LOW
MEDIUM
HIGH
NA
NA
NA
NA
HIGH
MEDIUM
(3) Tidal Marsh Channel Stability
(3) Streamside Area Attenuation
Function Class Rating Summary
(1) Hydrology
NA
HIGH
MEDIUM
HIGH
HIGH
NA
NO
MEDIUM
Stream Site Name Willow Greenway and Upper McDowell Creek Restoration Date of Evaluation
LOW
(4) Tidal Marsh Channel Stability
LOW
LOW
NA
NA
HIGH
NA
MEDIUM
NC SAM Stream Rating Sheet
Accompanies User Manual Version 2.1
LOW
MEDIUM
USACE/
All Streams
NCDWR
Intermittent
NA
NA
(2) Flood Flow
Addie Lasitter / Kimley-Horn
10/24/18
NO
NO
NO
Perennial
(2) Baseflow
Stream Category Assessor Name/Organization
MEDIUM
Pb2
USACE AID #:NCDWR #:
PROJECT / SITE INFORMATION:
1. Project name (if any):2. Date of evaluation:
3. Applicant/owner name:
5. County:6. Nearest named water body
7. River Basin: on USGS 7.5-minute quad:
8. Site coordinates (decimal degrees, at lower end of assessment reach):
STREAM INFORMATION: (depth and width can be approximations)
9. Site number (show on attached map):10. Length of assessment reach evaluated (feet):
11. Channel depth from bed (in riffle, if present) to top of bank (feet):Unable to assess channel depth.
12. Channel width at top of bank (feet):13. Is assessment reach a swamp stream?Yes No
14. Feature type:Perennial flow Intermittent flow Tidal Marsh Stream
STREAM RATING INFORMATION:
15. NC SAM Zone:Mountains (M)Piedmont (P)Inner Coastal Plain (I)Outer Coastal Plain (O)
16. Estimated geomorphic
valley shape (skip for a b
Tidal Marsh Stream):(more sinuous stream, flatter valley slope)(less sinuous stream, steeper valley slope)
17. Watershed size: (skip Size 1 (< 0.1 mi2)Size 2 (0.1 to < 0.5 mi2)Size 3 (0.5 to < 5 mi2)Size 4 (≥ 5 mi2)
for Tidal Marsh Stream)
ADDITIONAL INFORMATION:
18. Were regulatory considerations evaluated?Yes No If Yes, check all that appy to the assessment area.
Section 10 water Classified Trout Waters Water Supply Watershed (I II III IV V)
Essential Fish Habitat Primary Nursery Area High Quality Waters/Outstanding Resource Waters
Publicly owned property NCDWR riparian buffer rule in effect Nutrient Sensitive Waters
Anadromous fish 303(d) List CAMA Area of Environmental Concern (AEC)
Documented presence of a federal and/or state listed protected species within the assessment area.
List species:
Designated Critical Habitat (list species):
19. Are additional stream information/supplementary measurements included in "Notes/Sketch" section or attached?Yes No
1.Channel Water – assessment reach metric (skip for Size 1 streams and Tidal Marsh Streams)
A Water throughout assessment reach.
B No flow, water in pools only.
C No water in assessment reach.
2.Evidence of Flow Restriction – assessment reach metric
A At least 10% of assessment reach in-stream habitat or riffle-pool sequence is adversely affected by a flow restriction or fill to the
point of obstructing flow or a channel choked with aquatic macrophytes or ponded water or impounded on flood or ebb within
the assessment reach (examples: undersized or perched culverts, causeways that constrict the channel, tidal gates).
B Not A
3.Feature Pattern – assessment reach metric
A A majority of the assessment reach has altered pattern (examples: straightening, modification above or below culvert).
B Not A.
4.Feature Longitudinal Profile – assessment reach metric
A Majority of assessment reach has a substantially altered stream profile (examples: channel down-cutting, existing damming,
over widening, active aggradation, dredging, and excavation where appropriate channel profile has not reformed from any of
these disturbances).
B Not A
5.Signs of Active Instability – assessment reach metric
Consider only current instability, not past events from which the stream has currently recovered. Examples of instability include
active bank failure, active channel down-cutting (head-cut), active widening, and artificial hardening (such as concrete, gabion, rip-rap).
A < 10% of channel unstable
B 10 to 25% of channel unstable
C > 25% of channel unstable
6.Streamside Area Interaction – streamside area metric
Consider for the Left Bank (LB) and the Right Bank (RB).
LB RB
A A Little or no evidence of conditions that adversely affect reference interaction
B B Moderate evidence of conditions (examples: berms, levees, down-cutting, aggradation, dredging) that adversely affect
reference interaction (examples: limited streamside area access, disruption of flood flows through streamside area,
leaky or intermittent bulkheads, causeways with floodplain constriction, minor ditching [including mosquito ditching])
C C Extensive evidence of conditions that adversely affect reference interaction (little to no floodplain/intertidal zone access
[examples: causeways with floodplain and channel constriction, bulkheads, retaining walls, fill, stream incision,
disruption of flood flows through streamside area] or too much floodplain/intertidal zone access [examples:
impoundments, intensive mosquito ditching]) or floodplain/intertidal zone unnaturally absent or assessment reach is a
man-made feature on an interstream divide
7.Water Quality Stressors – assessment reach/intertidal zone metric
Check all that apply.
A Discolored water in stream or intertidal zone (milky white, blue, unnatural water discoloration, oil sheen, stream foam)
B Excessive sedimentation (burying of stream features or intertidal zone)
Willow Greenway and Upper McDowell Creek Restoration 10/24/18
35.471047, -80.872308
Stream 2 - McDowell Creek ~150
Town of Cornelius 4. Assessor name/organization:Addie Lasitter / Kimley-Horn
Mecklenburg
Catawba McDowell Creek
Manual for detailed descriptions and explanations of requested information. Record in the "Notes/Sketch" section if any supplementary
NOTE EVIDENCE OF STRESSORS AFFECTING THE ASSESSMENT AREA (do not need to be within the assessment area).
measurements were performed. See the NC SAM User Manual for examples of additional measurements that may be relevant.
NC SAM FIELD ASSESSMENT FORM
Accompanies User Manual Version 2.1
INSTRUCTIONS:Attach a sketch of the assessment area and photographs.Attach a copy of the USGS 7.5-minute topographic
quadrangle,and circle the location of the stream reach under evaluation.If multiple stream reaches will be evaluated on the same
property,identify and number all reaches on the attached map,and include a separate form for each reach.See the NC SAM User
4
10
C Noticeable evidence of pollutant discharges entering the assessment reach and causing a water quality problem
D Odor (not including natural sulfide odors)
E Current published or collected data indicating degraded water quality in the assessment reach. Cite source in the "Notes/Sketch"
section.
F Livestock with access to stream or intertidal zone
G Excessive algae in stream or intertidal zone
H Degraded marsh vegetation in the intertidal zone (removal, burning, regular mowing, destruction, etc.)
I Other:(explain in "Notes/Sketch" section)
J Little to no stressors
8.Recent Weather – watershed metric
For Size 1 or 2 streams, D1 drought or higher is considered a drought; for Size 3 or 4 streams, D2 drought or higher is considered a
drought.
A Drought conditions and no rainfall or rainfall not exceeding 1 inch within the last 48 hours
B Drought conditions and rainfall exceeding 1 inch within the last 48 hours
C No drought conditions
9 Large or Dangerous Stream – assessment reach metric
Yes No Is stream is too large or dangerous to assess? If Yes, skip to Metric 13 (Streamside Area Ground Surface Condition).
10.Natural In-stream Habitat Types – assessment reach metric
10a.Yes No Degraded in-stream habitat over majority of the assessment reach (examples of stressors include excessive
sedimentation, mining, excavation, in-stream hardening [for example, rip-rap], recent dredging, and snagging)
(evaluate for size 4 Coastal Plain streams only, then skip to Metric 12)
10b.Check all that occur (occurs if > 5% coverage of assessment reach) (skip for Size 4 Coastal Plain streams)
A Multiple aquatic macrophytes and aquatic mosses F 5% oysters or other natural hard bottoms
(include liverworts, lichens, and algal mats)G Submerged aquatic vegetation
B Multiple sticks and/or leaf packs and/or emergent H Low-tide refugia (pools)
vegetation I Sand bottom
C Multiple snags and logs (including lap trees)J 5% vertical bank along the marsh
D 5% undercut banks and/or root mats and/or roots K Little or no habitat
in banks extend to the normal wetted perimeter
E Little or no habitat
11.Bedform and Substrate – assessment reach metric (skip for Size 4 Coastal Plain streams and Tidal Marsh Streams)
11a.Yes No Is assessment reach in a natural sand-bed stream? (skip for Coastal Plain streams)
11b.Bedform evaluated. Check the appropriate box(es).
A Riffle-run section (evaluate 11c)
B Pool-glide section (evaluate 11d)
C Natural bedform absent (skip to Metric 12, Aquatic Life)
11c.In riffles sections, check all that occur below the normal wetted perimeter of the assessment reach – whether or not submerged.
Check at least one box in each row (skip for Size 4 Coastal Plain Streams and Tidal Marsh Streams). Not Present (NP) =
absent, Rare (R) = present but ≤ 10%, Common (C) = > 10-40%, Abundant (A) = > 40-70%, Predominant (P) = > 70%. Cumulative
percentages should not exceed 100% for each assessment reach.
NP R C A P
Bedrock/saprolite
Boulder (256 – 4096 mm)
Cobble (64 – 256 mm)
Gravel (2 – 64 mm)
Sand (.062 – 2 mm)
Silt/clay (< 0.062 mm)
Detritus
Artificial (rip-rap, concrete, etc.)
11d.Yes No Are pools filled with sediment? (skip for Size 4 Coastal Plain streams and Tidal Marsh Streams)
12.Aquatic Life – assessment reach metric (skip for Size 4 Coastal Plain streams and Tidal Marsh Streams)
12a.Yes No Was an in-stream aquatic life assessment performed as described in the User Manual?
If No, select one of the following reasons and skip to Metric 13. No Water Other:
12b.Yes No Are aquatic organisms present in the assessment reach (look in riffles, pools, then snags)? If Yes, check
all that apply. If No, skip to Metric 13.
1 >1 Numbers over columns refer to “individuals” for size 1 and 2 streams and “taxa” for size 3 and 4 streams.
Adult frogs
Aquatic reptiles
Aquatic macrophytes and aquatic mosses (include liverworts, lichens, and algal mats)
Beetles (including water pennies)
Caddisfly larvae (Trichoptera [T])
Asian clam (Corbicula )
Crustacean (isopod/amphipod/crayfish/shrimp)
Damselfly and dragonfly larvae
Dipterans (true flies)
Mayfly larvae (Ephemeroptera [E])
Megaloptera (alderfly, fishfly, dobsonfly larvae)
Midges/mosquito larvae
Mosquito fish (Gambusia ) or mud minnows (Umbra pygmaea)
Mussels/Clams (not Corbicula )
Other fish
Salamanders/tadpoles
Snails
Stonefly larvae (Plecoptera [P])
Tipulid larvae
*********************************REMAINING QUESTIONS ARE NOT APPLICABLE FOR TIDAL MARSH STREAMS****************************Check for TidalMarsh Streamsonly
Worms/leeches
13.Streamside Area Ground Surface Condition – streamside area metric (skip for Tidal Marsh Streams and B valley types)
Consider for the Left Bank (LB) and the Right Bank (RB). Consider storage capacity with regard to both overbank flow and
upland runoff.
LB RB
A A Little or no alteration to water storage capacity over a majority of the streamside area
B B Moderate alteration to water storage capacity over a majority of the streamside area
C C Severe alteration to water storage capacity over a majority of the streamside area (examples include: ditches, fill,
soil, compaction, livestock disturbance, buildings, man-made levees, drainage pipes)
14.Streamside Area Water Storage – streamside area metric (skip for Size 1 streams, Tidal Marsh Streams, and B valley types)
Consider for the Left Bank (LB) and the Right Bank (RB) of the streamside area.
LB RB
A A Majority of streamside area with depressions able to pond water ≥ 6 inches deep
B B Majority of streamside area with depressions able to pond water 3 to 6 inches deep
C C Majority of streamside area with depressions able to pond water < 3 inches deep
15.Wetland Presence – streamside area metric (skip for Tidal Marsh Streams)
Consider for the Left Bank (LB) and the Right Bank (RB). Do not consider wetlands outside of the streamside area or within the
normal wetted perimeter of assessment reach.
LB RB
Y Y Are wetlands present in the streamside area?
N N
16.Baseflow Contributors – assessment reach metric (skip for size 4 streams and Tidal Marsh Streams)
Check all contributors within the assessment reach or within view of and draining to the assessment reach.
A Streams and/or springs (jurisdictional discharges)
B Ponds (include wet detention basins; do not include sediment basins or dry detention basins)
C Obstruction that passes some flow during low-flow periods within assessment area (beaver dam, bottom-release dam)
D Evidence of bank seepage or sweating (iron oxidizing bacteria in water indicates seepage)
E Stream bed or bank soil reduced (dig through deposited sediment if present)
F None of the above
17.Baseflow Detractors – assessment area metric (skip for Tidal Marsh Streams)
Check all that apply.
A Evidence of substantial water withdrawals from the assessment reach (includes areas excavated for pump installation)
B Obstruction not passing flow during low flow periods affecting the assessment reach (ex: watertight dam, sediment deposit)
C Urban stream (≥ 24% impervious surface for watershed)
D Evidence that the stream-side area has been modified resulting in accelerated drainage into the assessment reach
E Assessment reach relocated to valley edge
F None of the above
18.Shading – assessment reach metric (skip for Tidal Marsh Streams)
Consider aspect. Consider “leaf-on” condition.
A Stream shading is appropriate for stream category (may include gaps associated with natural processes)
B Degraded (example: scattered trees)
C Stream shading is gone or largely absent
19.Buffer Width – streamside area metric (skip for Tidal Marsh Streams)
Consider “vegetated buffer” and “wooded buffer” separately for left bank (LB) and right bank (RB) starting at the top
of bank out to the first break.
Vegetated Wooded
LB RB LB RB
A A A A ≥ 100-feet wide or extends to the edge of the watershed
B B B B From 50 to < 100-feet wide
C C C C From 30 to < 50-feet wide
D D D D From 10 to < 30-feet wide
E E E E < 10-feet wide or no trees
20.Buffer Structure – streamside area metric (skip for Tidal Marsh Streams)
Consider for left bank (LB) and right bank (RB) for Metric 19 ("Vegetated" Buffer Width).
LB RB
A A Mature forest
B B Non-mature woody vegetation or modified vegetation structure
C C Herbaceous vegetation with or without a strip of trees < 10 feet wide
D D Maintained shrubs
E E Little or no vegetation
21.Buffer Stressors – streamside area metric (skip for Tidal Marsh Streams)
Check all appropriate boxes for left bank (LB) and right bank (RB). Indicate if listed stressor abuts stream (Abuts), does not abut but
is within 30 feet of stream (< 30 feet), or is between 30 to 50 feet of stream (30-50 feet).
If none of the following stressors occurs on either bank, check here and skip to Metric 22:
Abuts < 30 feet 30-50 feet
LB RB LB RB LB RB
A A A A A A Row crops
B B B B B B Maintained turf
C C C C C C Pasture (no livestock)/commercial horticulture
D D D D D D Pasture (active livestock use)
22.Stem Density – streamside area metric (skip for Tidal Marsh Streams)
Consider for left bank (LB) and right bank (RB) for Metric 19 ("Wooded" Buffer Width).
LB RB
A A Medium to high stem density
B B Low stem density
C C No wooded riparian buffer or predominantly herbaceous species or bare ground
23.Continuity of Vegetated Buffer – streamside area metric (skip for Tidal Marsh Streams)
Consider whether vegetated buffer is continuous along stream (parallel). Breaks are areas lacking vegetation > 10-feet wide.
LB RB
A A The total length of buffer breaks is < 25 percent.
B B The total length of buffer breaks is between 25 and 50 percent.
C C The total length of buffer breaks is > 50 percent.
24.Vegetative Composition – First 100 feet of streamside area metric (skip for Tidal Marsh Streams)
Evaluate the dominant vegetation within 100 feet of each bank or to the edge of the watershed (whichever comes first) as it contributes
to assessment reach habitat.
LB RB
A A Vegetation is close to undisturbed in species present and their proportions. Lower strata composed of native
species, with non-native invasive species absent or sparse.
B B Vegetation indicates disturbance in terms of species diversity or proportions, but is still largely composed of native
species. This may include communities of weedy native species that develop after clear-cutting or clearing or
communities with non-native invasive species present, but not dominant, over a large portion of the expected strata or
communities missing understory but retaining canopy trees.
C C Vegetation is severely disturbed in terms of species diversity or proportions. Mature canopy is absent or communities
with non-native invasive species dominant over a large portion of expected strata or communities composed of planted
stands of non-characteristic species or communities inappropriately composed of a single species or no vegetation.
25.Conductivity – assessment reach metric (skip for all Coastal Plain streams)
25a.Yes No Was a conductivity measurement recorded?
If No, select one of the following reasons. No Water Other:
25b.Check the box corresponding to the conductivity measurement (units of microsiemens per centimeter).
A <46 B 46 to < 67 C 67 to < 79 D 79 to < 230 E ≥ 230
Notes/Sketch:
Notes of Field Assessment Form (Y/N)
Presence of regulatory considerations (Y/N)
Additional stream information/supplementary measurements included (Y/N)
NC SAM feature type (perennial, intermittent, Tidal Marsh Stream)
(4) Floodplain Access
(4) Wooded Riparian Buffer
(4) Microtopography
(3) Stream Stability
(4) Channel Stability
(4) Sediment Transport
(4) Stream Geomorphology
(2) Stream/Intertidal Zone Interaction
(2) Longitudinal Tidal Flow
(2) Tidal Marsh Stream Stability
(3) Tidal Marsh Stream Geomorphology
(1) Water Quality
(2) Baseflow
(2) Streamside Area Vegetation
(3) Upland Pollutant Filtration
(3) Thermoregulation
(2) Indicators of Stressors
(2) Aquatic Life Tolerance
(2) Intertidal Zone Filtration
(1) Habitat
(2) In-stream Habitat
(3) Baseflow
(3) Substrate
(3) Stream Stability
(3) In-stream Habitat
(2) Stream-side Habitat
(3) Stream-side Habitat
(3) Thermoregulation
(2) Tidal Marsh In-stream Habitat
(3) Flow Restriction
(3) Tidal Marsh Stream Stability
(4) Tidal Marsh Stream Geomorphology
(3) Tidal Marsh In-stream Habitat
(2) Intertidal Zone Habitat
Overall LOW
LOW
MEDIUM
LOW
MEDIUM
MEDIUM
HIGH
NA
NA
MEDIUM
NA
LOW
MEDIUM
MEDIUM
NA
NA
NA
NA
HIGH
HIGH
(3) Tidal Marsh Channel Stability
(3) Streamside Area Attenuation
Function Class Rating Summary
(1) Hydrology
NA
LOW
HIGH
MEDIUM
HIGH
NA
NO
MEDIUM
Stream Site Name Willow Greenway and Upper McDowell Creek Restoration Date of Evaluation
LOW
(4) Tidal Marsh Channel Stability
LOW
LOW
NA
NA
LOW
NA
HIGH
NC SAM Stream Rating Sheet
Accompanies User Manual Version 2.1
LOW
MEDIUM
USACE/
All Streams
NCDWR
Intermittent
NA
NA
(2) Flood Flow
Addie Lasitter / Kimley-Horn
10/24/18
NO
NO
Perennial
(2) Baseflow
Stream Category Assessor Name/Organization
MEDIUM
Pb3
USACE AID #:NCDWR #:
PROJECT / SITE INFORMATION:
1. Project name (if any):2. Date of evaluation:
3. Applicant/owner name:
5. County:6. Nearest named water body
7. River Basin: on USGS 7.5-minute quad:
8. Site coordinates (decimal degrees, at lower end of assessment reach):
STREAM INFORMATION: (depth and width can be approximations)
9. Site number (show on attached map):10. Length of assessment reach evaluated (feet):
11. Channel depth from bed (in riffle, if present) to top of bank (feet):Unable to assess channel depth.
12. Channel width at top of bank (feet):13. Is assessment reach a swamp stream?Yes No
14. Feature type:Perennial flow Intermittent flow Tidal Marsh Stream
STREAM RATING INFORMATION:
15. NC SAM Zone:Mountains (M)Piedmont (P)Inner Coastal Plain (I)Outer Coastal Plain (O)
16. Estimated geomorphic
valley shape (skip for a b
Tidal Marsh Stream):(more sinuous stream, flatter valley slope)(less sinuous stream, steeper valley slope)
17. Watershed size: (skip Size 1 (< 0.1 mi2)Size 2 (0.1 to < 0.5 mi2)Size 3 (0.5 to < 5 mi2)Size 4 (≥ 5 mi2)
for Tidal Marsh Stream)
ADDITIONAL INFORMATION:
18. Were regulatory considerations evaluated?Yes No If Yes, check all that appy to the assessment area.
Section 10 water Classified Trout Waters Water Supply Watershed (I II III IV V)
Essential Fish Habitat Primary Nursery Area High Quality Waters/Outstanding Resource Waters
Publicly owned property NCDWR riparian buffer rule in effect Nutrient Sensitive Waters
Anadromous fish 303(d) List CAMA Area of Environmental Concern (AEC)
Documented presence of a federal and/or state listed protected species within the assessment area.
List species:
Designated Critical Habitat (list species):
19. Are additional stream information/supplementary measurements included in "Notes/Sketch" section or attached?Yes No
1.Channel Water – assessment reach metric (skip for Size 1 streams and Tidal Marsh Streams)
A Water throughout assessment reach.
B No flow, water in pools only.
C No water in assessment reach.
2.Evidence of Flow Restriction – assessment reach metric
A At least 10% of assessment reach in-stream habitat or riffle-pool sequence is adversely affected by a flow restriction or fill to the
point of obstructing flow or a channel choked with aquatic macrophytes or ponded water or impounded on flood or ebb within
the assessment reach (examples: undersized or perched culverts, causeways that constrict the channel, tidal gates).
B Not A
3.Feature Pattern – assessment reach metric
A A majority of the assessment reach has altered pattern (examples: straightening, modification above or below culvert).
B Not A.
4.Feature Longitudinal Profile – assessment reach metric
A Majority of assessment reach has a substantially altered stream profile (examples: channel down-cutting, existing damming,
over widening, active aggradation, dredging, and excavation where appropriate channel profile has not reformed from any of
these disturbances).
B Not A
5.Signs of Active Instability – assessment reach metric
Consider only current instability, not past events from which the stream has currently recovered. Examples of instability include
active bank failure, active channel down-cutting (head-cut), active widening, and artificial hardening (such as concrete, gabion, rip-rap).
A < 10% of channel unstable
B 10 to 25% of channel unstable
C > 25% of channel unstable
6.Streamside Area Interaction – streamside area metric
Consider for the Left Bank (LB) and the Right Bank (RB).
LB RB
A A Little or no evidence of conditions that adversely affect reference interaction
B B Moderate evidence of conditions (examples: berms, levees, down-cutting, aggradation, dredging) that adversely affect
reference interaction (examples: limited streamside area access, disruption of flood flows through streamside area,
leaky or intermittent bulkheads, causeways with floodplain constriction, minor ditching [including mosquito ditching])
C C Extensive evidence of conditions that adversely affect reference interaction (little to no floodplain/intertidal zone access
[examples: causeways with floodplain and channel constriction, bulkheads, retaining walls, fill, stream incision,
disruption of flood flows through streamside area] or too much floodplain/intertidal zone access [examples:
impoundments, intensive mosquito ditching]) or floodplain/intertidal zone unnaturally absent or assessment reach is a
man-made feature on an interstream divide
7.Water Quality Stressors – assessment reach/intertidal zone metric
Check all that apply.
A Discolored water in stream or intertidal zone (milky white, blue, unnatural water discoloration, oil sheen, stream foam)
B Excessive sedimentation (burying of stream features or intertidal zone)
Willow Greenway and Upper McDowell Creek Restoration 10/24/18
35.470403, -80.870084
Stream 3 ~150
Town of Cornelius 4. Assessor name/organization:Addie Lasitter / Kimley-Horn
Mecklenburg
Catawba McDowell Creek
Manual for detailed descriptions and explanations of requested information. Record in the "Notes/Sketch" section if any supplementary
NOTE EVIDENCE OF STRESSORS AFFECTING THE ASSESSMENT AREA (do not need to be within the assessment area).
measurements were performed. See the NC SAM User Manual for examples of additional measurements that may be relevant.
NC SAM FIELD ASSESSMENT FORM
Accompanies User Manual Version 2.1
INSTRUCTIONS:Attach a sketch of the assessment area and photographs.Attach a copy of the USGS 7.5-minute topographic
quadrangle,and circle the location of the stream reach under evaluation.If multiple stream reaches will be evaluated on the same
property,identify and number all reaches on the attached map,and include a separate form for each reach.See the NC SAM User
4
8
C Noticeable evidence of pollutant discharges entering the assessment reach and causing a water quality problem
D Odor (not including natural sulfide odors)
E Current published or collected data indicating degraded water quality in the assessment reach. Cite source in the "Notes/Sketch"
section.
F Livestock with access to stream or intertidal zone
G Excessive algae in stream or intertidal zone
H Degraded marsh vegetation in the intertidal zone (removal, burning, regular mowing, destruction, etc.)
I Other:(explain in "Notes/Sketch" section)
J Little to no stressors
8.Recent Weather – watershed metric
For Size 1 or 2 streams, D1 drought or higher is considered a drought; for Size 3 or 4 streams, D2 drought or higher is considered a
drought.
A Drought conditions and no rainfall or rainfall not exceeding 1 inch within the last 48 hours
B Drought conditions and rainfall exceeding 1 inch within the last 48 hours
C No drought conditions
9 Large or Dangerous Stream – assessment reach metric
Yes No Is stream is too large or dangerous to assess? If Yes, skip to Metric 13 (Streamside Area Ground Surface Condition).
10.Natural In-stream Habitat Types – assessment reach metric
10a.Yes No Degraded in-stream habitat over majority of the assessment reach (examples of stressors include excessive
sedimentation, mining, excavation, in-stream hardening [for example, rip-rap], recent dredging, and snagging)
(evaluate for size 4 Coastal Plain streams only, then skip to Metric 12)
10b.Check all that occur (occurs if > 5% coverage of assessment reach) (skip for Size 4 Coastal Plain streams)
A Multiple aquatic macrophytes and aquatic mosses F 5% oysters or other natural hard bottoms
(include liverworts, lichens, and algal mats)G Submerged aquatic vegetation
B Multiple sticks and/or leaf packs and/or emergent H Low-tide refugia (pools)
vegetation I Sand bottom
C Multiple snags and logs (including lap trees)J 5% vertical bank along the marsh
D 5% undercut banks and/or root mats and/or roots K Little or no habitat
in banks extend to the normal wetted perimeter
E Little or no habitat
11.Bedform and Substrate – assessment reach metric (skip for Size 4 Coastal Plain streams and Tidal Marsh Streams)
11a.Yes No Is assessment reach in a natural sand-bed stream? (skip for Coastal Plain streams)
11b.Bedform evaluated. Check the appropriate box(es).
A Riffle-run section (evaluate 11c)
B Pool-glide section (evaluate 11d)
C Natural bedform absent (skip to Metric 12, Aquatic Life)
11c.In riffles sections, check all that occur below the normal wetted perimeter of the assessment reach – whether or not submerged.
Check at least one box in each row (skip for Size 4 Coastal Plain Streams and Tidal Marsh Streams). Not Present (NP) =
absent, Rare (R) = present but ≤ 10%, Common (C) = > 10-40%, Abundant (A) = > 40-70%, Predominant (P) = > 70%. Cumulative
percentages should not exceed 100% for each assessment reach.
NP R C A P
Bedrock/saprolite
Boulder (256 – 4096 mm)
Cobble (64 – 256 mm)
Gravel (2 – 64 mm)
Sand (.062 – 2 mm)
Silt/clay (< 0.062 mm)
Detritus
Artificial (rip-rap, concrete, etc.)
11d.Yes No Are pools filled with sediment? (skip for Size 4 Coastal Plain streams and Tidal Marsh Streams)
12.Aquatic Life – assessment reach metric (skip for Size 4 Coastal Plain streams and Tidal Marsh Streams)
12a.Yes No Was an in-stream aquatic life assessment performed as described in the User Manual?
If No, select one of the following reasons and skip to Metric 13. No Water Other:
12b.Yes No Are aquatic organisms present in the assessment reach (look in riffles, pools, then snags)? If Yes, check
all that apply. If No, skip to Metric 13.
1 >1 Numbers over columns refer to “individuals” for size 1 and 2 streams and “taxa” for size 3 and 4 streams.
Adult frogs
Aquatic reptiles
Aquatic macrophytes and aquatic mosses (include liverworts, lichens, and algal mats)
Beetles (including water pennies)
Caddisfly larvae (Trichoptera [T])
Asian clam (Corbicula )
Crustacean (isopod/amphipod/crayfish/shrimp)
Damselfly and dragonfly larvae
Dipterans (true flies)
Mayfly larvae (Ephemeroptera [E])
Megaloptera (alderfly, fishfly, dobsonfly larvae)
Midges/mosquito larvae
Mosquito fish (Gambusia ) or mud minnows (Umbra pygmaea)
Mussels/Clams (not Corbicula )
Other fish
Salamanders/tadpoles
Snails
Stonefly larvae (Plecoptera [P])
Tipulid larvae
*********************************REMAINING QUESTIONS ARE NOT APPLICABLE FOR TIDAL MARSH STREAMS****************************Check for TidalMarsh Streamsonly
Worms/leeches
13.Streamside Area Ground Surface Condition – streamside area metric (skip for Tidal Marsh Streams and B valley types)
Consider for the Left Bank (LB) and the Right Bank (RB). Consider storage capacity with regard to both overbank flow and
upland runoff.
LB RB
A A Little or no alteration to water storage capacity over a majority of the streamside area
B B Moderate alteration to water storage capacity over a majority of the streamside area
C C Severe alteration to water storage capacity over a majority of the streamside area (examples include: ditches, fill,
soil, compaction, livestock disturbance, buildings, man-made levees, drainage pipes)
14.Streamside Area Water Storage – streamside area metric (skip for Size 1 streams, Tidal Marsh Streams, and B valley types)
Consider for the Left Bank (LB) and the Right Bank (RB) of the streamside area.
LB RB
A A Majority of streamside area with depressions able to pond water ≥ 6 inches deep
B B Majority of streamside area with depressions able to pond water 3 to 6 inches deep
C C Majority of streamside area with depressions able to pond water < 3 inches deep
15.Wetland Presence – streamside area metric (skip for Tidal Marsh Streams)
Consider for the Left Bank (LB) and the Right Bank (RB). Do not consider wetlands outside of the streamside area or within the
normal wetted perimeter of assessment reach.
LB RB
Y Y Are wetlands present in the streamside area?
N N
16.Baseflow Contributors – assessment reach metric (skip for size 4 streams and Tidal Marsh Streams)
Check all contributors within the assessment reach or within view of and draining to the assessment reach.
A Streams and/or springs (jurisdictional discharges)
B Ponds (include wet detention basins; do not include sediment basins or dry detention basins)
C Obstruction that passes some flow during low-flow periods within assessment area (beaver dam, bottom-release dam)
D Evidence of bank seepage or sweating (iron oxidizing bacteria in water indicates seepage)
E Stream bed or bank soil reduced (dig through deposited sediment if present)
F None of the above
17.Baseflow Detractors – assessment area metric (skip for Tidal Marsh Streams)
Check all that apply.
A Evidence of substantial water withdrawals from the assessment reach (includes areas excavated for pump installation)
B Obstruction not passing flow during low flow periods affecting the assessment reach (ex: watertight dam, sediment deposit)
C Urban stream (≥ 24% impervious surface for watershed)
D Evidence that the stream-side area has been modified resulting in accelerated drainage into the assessment reach
E Assessment reach relocated to valley edge
F None of the above
18.Shading – assessment reach metric (skip for Tidal Marsh Streams)
Consider aspect. Consider “leaf-on” condition.
A Stream shading is appropriate for stream category (may include gaps associated with natural processes)
B Degraded (example: scattered trees)
C Stream shading is gone or largely absent
19.Buffer Width – streamside area metric (skip for Tidal Marsh Streams)
Consider “vegetated buffer” and “wooded buffer” separately for left bank (LB) and right bank (RB) starting at the top
of bank out to the first break.
Vegetated Wooded
LB RB LB RB
A A A A ≥ 100-feet wide or extends to the edge of the watershed
B B B B From 50 to < 100-feet wide
C C C C From 30 to < 50-feet wide
D D D D From 10 to < 30-feet wide
E E E E < 10-feet wide or no trees
20.Buffer Structure – streamside area metric (skip for Tidal Marsh Streams)
Consider for left bank (LB) and right bank (RB) for Metric 19 ("Vegetated" Buffer Width).
LB RB
A A Mature forest
B B Non-mature woody vegetation or modified vegetation structure
C C Herbaceous vegetation with or without a strip of trees < 10 feet wide
D D Maintained shrubs
E E Little or no vegetation
21.Buffer Stressors – streamside area metric (skip for Tidal Marsh Streams)
Check all appropriate boxes for left bank (LB) and right bank (RB). Indicate if listed stressor abuts stream (Abuts), does not abut but
is within 30 feet of stream (< 30 feet), or is between 30 to 50 feet of stream (30-50 feet).
If none of the following stressors occurs on either bank, check here and skip to Metric 22:
Abuts < 30 feet 30-50 feet
LB RB LB RB LB RB
A A A A A A Row crops
B B B B B B Maintained turf
C C C C C C Pasture (no livestock)/commercial horticulture
D D D D D D Pasture (active livestock use)
22.Stem Density – streamside area metric (skip for Tidal Marsh Streams)
Consider for left bank (LB) and right bank (RB) for Metric 19 ("Wooded" Buffer Width).
LB RB
A A Medium to high stem density
B B Low stem density
C C No wooded riparian buffer or predominantly herbaceous species or bare ground
23.Continuity of Vegetated Buffer – streamside area metric (skip for Tidal Marsh Streams)
Consider whether vegetated buffer is continuous along stream (parallel). Breaks are areas lacking vegetation > 10-feet wide.
LB RB
A A The total length of buffer breaks is < 25 percent.
B B The total length of buffer breaks is between 25 and 50 percent.
C C The total length of buffer breaks is > 50 percent.
24.Vegetative Composition – First 100 feet of streamside area metric (skip for Tidal Marsh Streams)
Evaluate the dominant vegetation within 100 feet of each bank or to the edge of the watershed (whichever comes first) as it contributes
to assessment reach habitat.
LB RB
A A Vegetation is close to undisturbed in species present and their proportions. Lower strata composed of native
species, with non-native invasive species absent or sparse.
B B Vegetation indicates disturbance in terms of species diversity or proportions, but is still largely composed of native
species. This may include communities of weedy native species that develop after clear-cutting or clearing or
communities with non-native invasive species present, but not dominant, over a large portion of the expected strata or
communities missing understory but retaining canopy trees.
C C Vegetation is severely disturbed in terms of species diversity or proportions. Mature canopy is absent or communities
with non-native invasive species dominant over a large portion of expected strata or communities composed of planted
stands of non-characteristic species or communities inappropriately composed of a single species or no vegetation.
25.Conductivity – assessment reach metric (skip for all Coastal Plain streams)
25a.Yes No Was a conductivity measurement recorded?
If No, select one of the following reasons. No Water Other:
25b.Check the box corresponding to the conductivity measurement (units of microsiemens per centimeter).
A <46 B 46 to < 67 C 67 to < 79 D 79 to < 230 E ≥ 230
Notes/Sketch:
Notes of Field Assessment Form (Y/N)
Presence of regulatory considerations (Y/N)
Additional stream information/supplementary measurements included (Y/N)
NC SAM feature type (perennial, intermittent, Tidal Marsh Stream)
(4) Floodplain Access
(4) Wooded Riparian Buffer
(4) Microtopography
(3) Stream Stability
(4) Channel Stability
(4) Sediment Transport
(4) Stream Geomorphology
(2) Stream/Intertidal Zone Interaction
(2) Longitudinal Tidal Flow
(2) Tidal Marsh Stream Stability
(3) Tidal Marsh Stream Geomorphology
(1) Water Quality
(2) Baseflow
(2) Streamside Area Vegetation
(3) Upland Pollutant Filtration
(3) Thermoregulation
(2) Indicators of Stressors
(2) Aquatic Life Tolerance
(2) Intertidal Zone Filtration
(1) Habitat
(2) In-stream Habitat
(3) Baseflow
(3) Substrate
(3) Stream Stability
(3) In-stream Habitat
(2) Stream-side Habitat
(3) Stream-side Habitat
(3) Thermoregulation
(2) Tidal Marsh In-stream Habitat
(3) Flow Restriction
(3) Tidal Marsh Stream Stability
(4) Tidal Marsh Stream Geomorphology
(3) Tidal Marsh In-stream Habitat
(2) Intertidal Zone Habitat
Overall MEDIUM
MEDIUM
MEDIUM
LOW
MEDIUM
LOW
HIGH
NA
NA
MEDIUM
NA
MEDIUM
MEDIUM
HIGH
NA
NA
NA
NA
HIGH
MEDIUM
(3) Tidal Marsh Channel Stability
(3) Streamside Area Attenuation
Function Class Rating Summary
(1) Hydrology
NA
HIGH
MEDIUM
MEDIUM
HIGH
NA
NO
MEDIUM
Stream Site Name Willow Greenway and Upper McDowell Creek Restoration Date of Evaluation
MEDIUM
(4) Tidal Marsh Channel Stability
MEDIUM
LOW
NA
NA
HIGH
NA
MEDIUM
NC SAM Stream Rating Sheet
Accompanies User Manual Version 2.1
LOW
HIGH
USACE/
All Streams
NCDWR
Intermittent
NA
NA
(2) Flood Flow
Addie Lasitter / Kimley-Horn
10/24/18
NO
NO
NO
Perennial
(2) Baseflow
Stream Category Assessor Name/Organization
MEDIUM
Pb1
USACE AID #:NCDWR #:
PROJECT / SITE INFORMATION:
1. Project name (if any):2. Date of evaluation:
3. Applicant/owner name:
5. County:6. Nearest named water body
7. River Basin: on USGS 7.5-minute quad:
8. Site coordinates (decimal degrees, at lower end of assessment reach):
STREAM INFORMATION: (depth and width can be approximations)
9. Site number (show on attached map):10. Length of assessment reach evaluated (feet):
11. Channel depth from bed (in riffle, if present) to top of bank (feet):Unable to assess channel depth.
12. Channel width at top of bank (feet):13. Is assessment reach a swamp stream?Yes No
14. Feature type:Perennial flow Intermittent flow Tidal Marsh Stream
STREAM RATING INFORMATION:
15. NC SAM Zone:Mountains (M)Piedmont (P)Inner Coastal Plain (I)Outer Coastal Plain (O)
16. Estimated geomorphic
valley shape (skip for a b
Tidal Marsh Stream):(more sinuous stream, flatter valley slope)(less sinuous stream, steeper valley slope)
17. Watershed size: (skip Size 1 (< 0.1 mi2)Size 2 (0.1 to < 0.5 mi2)Size 3 (0.5 to < 5 mi2)Size 4 (≥ 5 mi2)
for Tidal Marsh Stream)
ADDITIONAL INFORMATION:
18. Were regulatory considerations evaluated?Yes No If Yes, check all that appy to the assessment area.
Section 10 water Classified Trout Waters Water Supply Watershed (I II III IV V)
Essential Fish Habitat Primary Nursery Area High Quality Waters/Outstanding Resource Waters
Publicly owned property NCDWR riparian buffer rule in effect Nutrient Sensitive Waters
Anadromous fish 303(d) List CAMA Area of Environmental Concern (AEC)
Documented presence of a federal and/or state listed protected species within the assessment area.
List species:
Designated Critical Habitat (list species):
19. Are additional stream information/supplementary measurements included in "Notes/Sketch" section or attached?Yes No
1.Channel Water – assessment reach metric (skip for Size 1 streams and Tidal Marsh Streams)
A Water throughout assessment reach.
B No flow, water in pools only.
C No water in assessment reach.
2.Evidence of Flow Restriction – assessment reach metric
A At least 10% of assessment reach in-stream habitat or riffle-pool sequence is adversely affected by a flow restriction or fill to the
point of obstructing flow or a channel choked with aquatic macrophytes or ponded water or impounded on flood or ebb within
the assessment reach (examples: undersized or perched culverts, causeways that constrict the channel, tidal gates).
B Not A
3.Feature Pattern – assessment reach metric
A A majority of the assessment reach has altered pattern (examples: straightening, modification above or below culvert).
B Not A.
4.Feature Longitudinal Profile – assessment reach metric
A Majority of assessment reach has a substantially altered stream profile (examples: channel down-cutting, existing damming,
over widening, active aggradation, dredging, and excavation where appropriate channel profile has not reformed from any of
these disturbances).
B Not A
5.Signs of Active Instability – assessment reach metric
Consider only current instability, not past events from which the stream has currently recovered. Examples of instability include
active bank failure, active channel down-cutting (head-cut), active widening, and artificial hardening (such as concrete, gabion, rip-rap).
A < 10% of channel unstable
B 10 to 25% of channel unstable
C > 25% of channel unstable
6.Streamside Area Interaction – streamside area metric
Consider for the Left Bank (LB) and the Right Bank (RB).
LB RB
A A Little or no evidence of conditions that adversely affect reference interaction
B B Moderate evidence of conditions (examples: berms, levees, down-cutting, aggradation, dredging) that adversely affect
reference interaction (examples: limited streamside area access, disruption of flood flows through streamside area,
leaky or intermittent bulkheads, causeways with floodplain constriction, minor ditching [including mosquito ditching])
C C Extensive evidence of conditions that adversely affect reference interaction (little to no floodplain/intertidal zone access
[examples: causeways with floodplain and channel constriction, bulkheads, retaining walls, fill, stream incision,
disruption of flood flows through streamside area] or too much floodplain/intertidal zone access [examples:
impoundments, intensive mosquito ditching]) or floodplain/intertidal zone unnaturally absent or assessment reach is a
man-made feature on an interstream divide
7.Water Quality Stressors – assessment reach/intertidal zone metric
Check all that apply.
A Discolored water in stream or intertidal zone (milky white, blue, unnatural water discoloration, oil sheen, stream foam)
B Excessive sedimentation (burying of stream features or intertidal zone)
Willow Greenway and Upper McDowell Creek Restoration 10/24/18
35.251821, -80.881138
Stream 4 ~150
Town of Cornelius 4. Assessor name/organization:Addie Lasitter / Kimley-Horn
Mecklenburg
Catawba McDowell Creek
Manual for detailed descriptions and explanations of requested information. Record in the "Notes/Sketch" section if any supplementary
NOTE EVIDENCE OF STRESSORS AFFECTING THE ASSESSMENT AREA (do not need to be within the assessment area).
measurements were performed. See the NC SAM User Manual for examples of additional measurements that may be relevant.
NC SAM FIELD ASSESSMENT FORM
Accompanies User Manual Version 2.1
INSTRUCTIONS:Attach a sketch of the assessment area and photographs.Attach a copy of the USGS 7.5-minute topographic
quadrangle,and circle the location of the stream reach under evaluation.If multiple stream reaches will be evaluated on the same
property,identify and number all reaches on the attached map,and include a separate form for each reach.See the NC SAM User
3
6
C Noticeable evidence of pollutant discharges entering the assessment reach and causing a water quality problem
D Odor (not including natural sulfide odors)
E Current published or collected data indicating degraded water quality in the assessment reach. Cite source in the "Notes/Sketch"
section.
F Livestock with access to stream or intertidal zone
G Excessive algae in stream or intertidal zone
H Degraded marsh vegetation in the intertidal zone (removal, burning, regular mowing, destruction, etc.)
I Other:(explain in "Notes/Sketch" section)
J Little to no stressors
8.Recent Weather – watershed metric
For Size 1 or 2 streams, D1 drought or higher is considered a drought; for Size 3 or 4 streams, D2 drought or higher is considered a
drought.
A Drought conditions and no rainfall or rainfall not exceeding 1 inch within the last 48 hours
B Drought conditions and rainfall exceeding 1 inch within the last 48 hours
C No drought conditions
9 Large or Dangerous Stream – assessment reach metric
Yes No Is stream is too large or dangerous to assess? If Yes, skip to Metric 13 (Streamside Area Ground Surface Condition).
10.Natural In-stream Habitat Types – assessment reach metric
10a.Yes No Degraded in-stream habitat over majority of the assessment reach (examples of stressors include excessive
sedimentation, mining, excavation, in-stream hardening [for example, rip-rap], recent dredging, and snagging)
(evaluate for size 4 Coastal Plain streams only, then skip to Metric 12)
10b.Check all that occur (occurs if > 5% coverage of assessment reach) (skip for Size 4 Coastal Plain streams)
A Multiple aquatic macrophytes and aquatic mosses F 5% oysters or other natural hard bottoms
(include liverworts, lichens, and algal mats)G Submerged aquatic vegetation
B Multiple sticks and/or leaf packs and/or emergent H Low-tide refugia (pools)
vegetation I Sand bottom
C Multiple snags and logs (including lap trees)J 5% vertical bank along the marsh
D 5% undercut banks and/or root mats and/or roots K Little or no habitat
in banks extend to the normal wetted perimeter
E Little or no habitat
11.Bedform and Substrate – assessment reach metric (skip for Size 4 Coastal Plain streams and Tidal Marsh Streams)
11a.Yes No Is assessment reach in a natural sand-bed stream? (skip for Coastal Plain streams)
11b.Bedform evaluated. Check the appropriate box(es).
A Riffle-run section (evaluate 11c)
B Pool-glide section (evaluate 11d)
C Natural bedform absent (skip to Metric 12, Aquatic Life)
11c.In riffles sections, check all that occur below the normal wetted perimeter of the assessment reach – whether or not submerged.
Check at least one box in each row (skip for Size 4 Coastal Plain Streams and Tidal Marsh Streams). Not Present (NP) =
absent, Rare (R) = present but ≤ 10%, Common (C) = > 10-40%, Abundant (A) = > 40-70%, Predominant (P) = > 70%. Cumulative
percentages should not exceed 100% for each assessment reach.
NP R C A P
Bedrock/saprolite
Boulder (256 – 4096 mm)
Cobble (64 – 256 mm)
Gravel (2 – 64 mm)
Sand (.062 – 2 mm)
Silt/clay (< 0.062 mm)
Detritus
Artificial (rip-rap, concrete, etc.)
11d.Yes No Are pools filled with sediment? (skip for Size 4 Coastal Plain streams and Tidal Marsh Streams)
12.Aquatic Life – assessment reach metric (skip for Size 4 Coastal Plain streams and Tidal Marsh Streams)
12a.Yes No Was an in-stream aquatic life assessment performed as described in the User Manual?
If No, select one of the following reasons and skip to Metric 13. No Water Other:
12b.Yes No Are aquatic organisms present in the assessment reach (look in riffles, pools, then snags)? If Yes, check
all that apply. If No, skip to Metric 13.
1 >1 Numbers over columns refer to “individuals” for size 1 and 2 streams and “taxa” for size 3 and 4 streams.
Adult frogs
Aquatic reptiles
Aquatic macrophytes and aquatic mosses (include liverworts, lichens, and algal mats)
Beetles (including water pennies)
Caddisfly larvae (Trichoptera [T])
Asian clam (Corbicula )
Crustacean (isopod/amphipod/crayfish/shrimp)
Damselfly and dragonfly larvae
Dipterans (true flies)
Mayfly larvae (Ephemeroptera [E])
Megaloptera (alderfly, fishfly, dobsonfly larvae)
Midges/mosquito larvae
Mosquito fish (Gambusia ) or mud minnows (Umbra pygmaea)
Mussels/Clams (not Corbicula )
Other fish
Salamanders/tadpoles
Snails
Stonefly larvae (Plecoptera [P])
Tipulid larvae
*********************************REMAINING QUESTIONS ARE NOT APPLICABLE FOR TIDAL MARSH STREAMS****************************Check for TidalMarsh Streamsonly
Worms/leeches
13.Streamside Area Ground Surface Condition – streamside area metric (skip for Tidal Marsh Streams and B valley types)
Consider for the Left Bank (LB) and the Right Bank (RB). Consider storage capacity with regard to both overbank flow and
upland runoff.
LB RB
A A Little or no alteration to water storage capacity over a majority of the streamside area
B B Moderate alteration to water storage capacity over a majority of the streamside area
C C Severe alteration to water storage capacity over a majority of the streamside area (examples include: ditches, fill,
soil, compaction, livestock disturbance, buildings, man-made levees, drainage pipes)
14.Streamside Area Water Storage – streamside area metric (skip for Size 1 streams, Tidal Marsh Streams, and B valley types)
Consider for the Left Bank (LB) and the Right Bank (RB) of the streamside area.
LB RB
A A Majority of streamside area with depressions able to pond water ≥ 6 inches deep
B B Majority of streamside area with depressions able to pond water 3 to 6 inches deep
C C Majority of streamside area with depressions able to pond water < 3 inches deep
15.Wetland Presence – streamside area metric (skip for Tidal Marsh Streams)
Consider for the Left Bank (LB) and the Right Bank (RB). Do not consider wetlands outside of the streamside area or within the
normal wetted perimeter of assessment reach.
LB RB
Y Y Are wetlands present in the streamside area?
N N
16.Baseflow Contributors – assessment reach metric (skip for size 4 streams and Tidal Marsh Streams)
Check all contributors within the assessment reach or within view of and draining to the assessment reach.
A Streams and/or springs (jurisdictional discharges)
B Ponds (include wet detention basins; do not include sediment basins or dry detention basins)
C Obstruction that passes some flow during low-flow periods within assessment area (beaver dam, bottom-release dam)
D Evidence of bank seepage or sweating (iron oxidizing bacteria in water indicates seepage)
E Stream bed or bank soil reduced (dig through deposited sediment if present)
F None of the above
17.Baseflow Detractors – assessment area metric (skip for Tidal Marsh Streams)
Check all that apply.
A Evidence of substantial water withdrawals from the assessment reach (includes areas excavated for pump installation)
B Obstruction not passing flow during low flow periods affecting the assessment reach (ex: watertight dam, sediment deposit)
C Urban stream (≥ 24% impervious surface for watershed)
D Evidence that the stream-side area has been modified resulting in accelerated drainage into the assessment reach
E Assessment reach relocated to valley edge
F None of the above
18.Shading – assessment reach metric (skip for Tidal Marsh Streams)
Consider aspect. Consider “leaf-on” condition.
A Stream shading is appropriate for stream category (may include gaps associated with natural processes)
B Degraded (example: scattered trees)
C Stream shading is gone or largely absent
19.Buffer Width – streamside area metric (skip for Tidal Marsh Streams)
Consider “vegetated buffer” and “wooded buffer” separately for left bank (LB) and right bank (RB) starting at the top
of bank out to the first break.
Vegetated Wooded
LB RB LB RB
A A A A ≥ 100-feet wide or extends to the edge of the watershed
B B B B From 50 to < 100-feet wide
C C C C From 30 to < 50-feet wide
D D D D From 10 to < 30-feet wide
E E E E < 10-feet wide or no trees
20.Buffer Structure – streamside area metric (skip for Tidal Marsh Streams)
Consider for left bank (LB) and right bank (RB) for Metric 19 ("Vegetated" Buffer Width).
LB RB
A A Mature forest
B B Non-mature woody vegetation or modified vegetation structure
C C Herbaceous vegetation with or without a strip of trees < 10 feet wide
D D Maintained shrubs
E E Little or no vegetation
21.Buffer Stressors – streamside area metric (skip for Tidal Marsh Streams)
Check all appropriate boxes for left bank (LB) and right bank (RB). Indicate if listed stressor abuts stream (Abuts), does not abut but
is within 30 feet of stream (< 30 feet), or is between 30 to 50 feet of stream (30-50 feet).
If none of the following stressors occurs on either bank, check here and skip to Metric 22:
Abuts < 30 feet 30-50 feet
LB RB LB RB LB RB
A A A A A A Row crops
B B B B B B Maintained turf
C C C C C C Pasture (no livestock)/commercial horticulture
D D D D D D Pasture (active livestock use)
22.Stem Density – streamside area metric (skip for Tidal Marsh Streams)
Consider for left bank (LB) and right bank (RB) for Metric 19 ("Wooded" Buffer Width).
LB RB
A A Medium to high stem density
B B Low stem density
C C No wooded riparian buffer or predominantly herbaceous species or bare ground
23.Continuity of Vegetated Buffer – streamside area metric (skip for Tidal Marsh Streams)
Consider whether vegetated buffer is continuous along stream (parallel). Breaks are areas lacking vegetation > 10-feet wide.
LB RB
A A The total length of buffer breaks is < 25 percent.
B B The total length of buffer breaks is between 25 and 50 percent.
C C The total length of buffer breaks is > 50 percent.
24.Vegetative Composition – First 100 feet of streamside area metric (skip for Tidal Marsh Streams)
Evaluate the dominant vegetation within 100 feet of each bank or to the edge of the watershed (whichever comes first) as it contributes
to assessment reach habitat.
LB RB
A A Vegetation is close to undisturbed in species present and their proportions. Lower strata composed of native
species, with non-native invasive species absent or sparse.
B B Vegetation indicates disturbance in terms of species diversity or proportions, but is still largely composed of native
species. This may include communities of weedy native species that develop after clear-cutting or clearing or
communities with non-native invasive species present, but not dominant, over a large portion of the expected strata or
communities missing understory but retaining canopy trees.
C C Vegetation is severely disturbed in terms of species diversity or proportions. Mature canopy is absent or communities
with non-native invasive species dominant over a large portion of expected strata or communities composed of planted
stands of non-characteristic species or communities inappropriately composed of a single species or no vegetation.
25.Conductivity – assessment reach metric (skip for all Coastal Plain streams)
25a.Yes No Was a conductivity measurement recorded?
If No, select one of the following reasons. No Water Other:
25b.Check the box corresponding to the conductivity measurement (units of microsiemens per centimeter).
A <46 B 46 to < 67 C 67 to < 79 D 79 to < 230 E ≥ 230
Notes/Sketch:
Notes of Field Assessment Form (Y/N)
Presence of regulatory considerations (Y/N)
Additional stream information/supplementary measurements included (Y/N)
NC SAM feature type (perennial, intermittent, Tidal Marsh Stream)
(4) Floodplain Access
(4) Wooded Riparian Buffer
(4) Microtopography
(3) Stream Stability
(4) Channel Stability
(4) Sediment Transport
(4) Stream Geomorphology
(2) Stream/Intertidal Zone Interaction
(2) Longitudinal Tidal Flow
(2) Tidal Marsh Stream Stability
(3) Tidal Marsh Stream Geomorphology
(1) Water Quality
(2) Baseflow
(2) Streamside Area Vegetation
(3) Upland Pollutant Filtration
(3) Thermoregulation
(2) Indicators of Stressors
(2) Aquatic Life Tolerance
(2) Intertidal Zone Filtration
(1) Habitat
(2) In-stream Habitat
(3) Baseflow
(3) Substrate
(3) Stream Stability
(3) In-stream Habitat
(2) Stream-side Habitat
(3) Stream-side Habitat
(3) Thermoregulation
(2) Tidal Marsh In-stream Habitat
(3) Flow Restriction
(3) Tidal Marsh Stream Stability
(4) Tidal Marsh Stream Geomorphology
(3) Tidal Marsh In-stream Habitat
(2) Intertidal Zone Habitat
Overall LOW
LOW
MEDIUM
LOW
LOW
MEDIUM
LOW
LOW
MEDIUM
LOW
LOW
LOW
LOW
LOW
MEDIUM
LOW
MEDIUM
NA
NA
LOW
NA
LOW
LOW
MEDIUM
NA
NA
NA
NA
MEDIUM
NO
NA
NA
MEDIUM
MEDIUM
NA
NA
NA
LOW
(3) Tidal Marsh Channel Stability
(3) Streamside Area Attenuation
Function Class Rating Summary
(1) Hydrology
MEDIUM
MEDIUM
NA
NA
NA
NA
NA
MEDIUM
MEDIUM
LOW
LOW
LOW
MEDIUM
LOW
NA
NO
NA
NA
MEDIUM
Stream Site Name
LOW
NA
Willow Greenway and Upper McDowell Creek Restoration Date of Evaluation
LOW
(4) Tidal Marsh Channel Stability
NA
NA
LOW
LOW
LOW
LOW
MEDIUM
MEDIUM
NA
NA
HIGH
NA
MEDIUM
NC SAM Stream Rating Sheet
Accompanies User Manual Version 2.1
LOW
LOW
USACE/
All Streams
NCDWR
Intermittent
NA
NA
(2) Flood Flow
Addie Lasitter / Kimley-Horn
10/24/18
NO
NO
NO
Intermittent
NA
LOW
LOW
LOW
(2) Baseflow
Stream Category Assessor Name/Organization
LOW
Pb1
Project/Site:Sampling Date:
Applicant/Owner:State:Sampling Point:
Investigator(s):
Landform (hillside, terrace, etc.):
Subregion (LRR or MLRA): Lat: Long:
Soil Map Unit Name:
X
Are Vegetation , Soil , or Hydrology Yes X
Are Vegetation , Soil , or Hydrology
SUMMARY OF FINDINGS – Attach site map showing sampling point locations, transects, important features, etc.
X No
No X X
No X
Yes
Yes
Yes X
No hydrology indicators present.
Sediment Deposits (B2)
Drift Deposits (B3)
Remarks:
Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available:
Depth (inches):
Depth (inches):
Depth (inches):
No
Saturation Present?
(includes capillary fringe)
Surface Water Present?
Field Observations:
Yes NoAre climatic / hydrologic conditions on the site typical for this time of year?(If no, explain in Remarks.)
significantly disturbed?
naturally problematic?
Are “Normal Circumstances” present?
(If needed, explain any answers in Remarks.)
Remarks:

Is the Sampled AreaYes
Yes
Yes
Hydric Soil Present?
Hydrophytic Vegetation Present?
Wetland Hydrology Present?
Nowithin a Wetland? Yes
City/County:Willow Greenway and Upper McDowell Creek Restoration Cornelius / Mecklenburg
W1-Up
10/24/18
Town of Cornelius NC
No
Section, Township, Range:Addie Lasitter
2NoneTerrace
Datum: WGS84-80.87003535.470103LRR P, MLRA 136
NWI classification:MO
Slope (%):Local relief (concave, convex, none):
Surface Water (A1)
High Water Table (A2)
Saturation (A3)
Water Marks (B1)
Wetland Hydrology Indicators:
True Aquatic Plants (B14)
Saturation Visible on Aerial Imagery (C9)
Secondary Indicators (minimum of two required)
W1-Up sample point taken upslope of W1-Wet on terrace, about 1' up in elevation from W1-Wet. No hydrology indicators or hydric soils present. FAC
vegetation present in upland area.
HYDROLOGY
Geomorphic Position (D2)
Shallow Aquitard (D3)
Hydrogen Sulfide Odor (C1)
Oxidized Rhizospheres on Living Roots (C3)
Presence of Reduced Iron (C4)
Recent Iron Reduction in Tilled Soils (C6)
Thin Muck Surface (C7)
Other (Explain in Remarks)
Iron Deposits (B5)
U.S. Army Corps of Engineers
WETLAND DETERMINATION DATA SHEET – Eastern Mountains and Piedmont Region
See ERDC/EL TR-07-24; the proponent agency is CECW-CO-R
OMB Control #: 0710-xxxx, Exp: Pending
Requirement Control Symbol EXEMPT:
(Authority: AR 335-15, paragraph 5-2a)
Microtopographic Relief (D4)
FAC-Neutral Test (D5)
Inundation Visible on Aerial Imagery (B7)
Water-Stained Leaves (B9)
Aquatic Fauna (B13)
Algal Mat or Crust (B4)
Wetland Hydrology Present?
Stunted or Stressed Plants (D1)
NoYes
No
No
Water Table Present?
Primary Indicators (minimum of one is required; check all that apply) Surface Soil Cracks (B6)
Sparsely Vegetated Concave Surface (B8)
Drainage Patterns (B10)
Moss Trim Lines (B16)
Dry-Season Water Table (C2)
Crayfish Burrows (C8)
ENG FORM 6116-4-SG, JUL 2018 Eastern Mountains and Piedmont – Version 2.0
Sampling Point:
(Plot size:
1.
2.
3.
4.
5.
6.(A/B)
7.
50% of total cover: 20% of total cover:x 1 =
Sapling/Shrub Stratum (Plot size:x 2 =
1.x 3 =
2.x 4 =
3.x 5 =
4.Column Totals:(B)
5.
6.
7.
8.X
9.
4 - Morphological Adaptations1 (Provide supporting
50% of total cover: 20% of total cover:
Herb Stratum (Plot size:
1.
2.
3.
4.
5.
6.
7.
8.
9.
10.
11.
50% of total cover: 20% of total cover:
Woody Vine Stratum (Plot size:
1.
2.
3.
4.
5.
50% of total cover: 20% of total cover:Yes X
3 - Prevalence Index is ≤3.01
data in Remarks or on a separate sheet)
Problematic Hydrophytic Vegetation1 (Explain)
No
W1-Up
4
5
FACU species
UPL species
Hydrophytic Vegetation Indicators:
0
217
0
64
Total Number of Dominant
Species Across All Strata:
Dominance Test worksheet:
Number of Dominant Species
That Are OBL, FACW, or FAC:
FAC
OBL species
FACW species
FAC species
Sapling/Shrub – Woody plants, excluding vines, less
than 3 in. DBH and greater than or equal to 3.28 ft
(1 m) tall.
Tree – Woody plants, excluding vines, 3 in. (7.6 cm) or
more in diameter at breast height (DBH), regardless of
height.
1Indicators of hydric soil and wetland hydrology must be
present, unless disturbed or problematic.
Absolute
% Cover
80.0%
Percent of Dominant Species
That Are OBL, FACW, or FAC:
12
Acer rubrum
Tree Stratum
)
=Total Cover
Quercus nigra
Quercus phellos
30 )
25
Indicator
Status
15
10
Dominant
Species?
Yes
5
7
Quercus nigra
Trifolium repens 25
15
Definitions of Four Vegetation Strata:
Woody Vine – All woody vines greater than 3.28 ft in
height.
Hydrophytic
Vegetation
Present?
=Total Cover
Herb – All herbaceous (non-woody) plants, regardless
of size, and woody plants less than 3.28 ft tall.
30 )
Campsis radicans
25
5
36
13
Prevalence Index worksheet:
Total % Cover of:
39
25
(A)
(B)
(A)
117
0
100
Multiply by:
0
3.39Prevalence Index = B/A =
0
Yes FAC
1 - Rapid Test for Hydrophytic Vegetation
2 - Dominance Test is >50%
VEGETATION (Four Strata)– Use scientific names of plants.
13 5 0
Yes
Yes
FAC
FAC
Remarks: (Include photo numbers here or on a separate sheet.)
)5
=Total Cover
FACUYes
11
=Total Cover2
2 No FAC
ENG FORM 6116-4-SG, JUL 2018 Eastern Mountains and Piedmont – Version 2.0
Depth (inches):X
Dark Surface (S7)unless disturbed or problematic.Red Parent Material (F21) (MLRA 127, 147, 148)
No
Hydric Soil Indicators:
Polyvalue Below Surface (S8) (MLRA 147, 148)
Thin Dark Surface (S9) (MLRA 147, 148)
Loamy Gleyed Matrix (F2)
Redox Dark Surface (F6)
Redox Depressions (F8)
Loamy Mucky Mineral (F1) (MLRA 136)
Depleted Matrix (F3)
Depleted Dark Surface (F7)
2 cm Muck (A10) (MLRA 147)
Coast Prairie Redox (A16)
Indicators for Problematic Hydric Soils3:
(MLRA 147, 148)
Piedmont Floodplain Soils (F19)
(MLRA 136, 147)
Very Shallow Dark Surface (F22)
Red Parent Material (F21)
(outside MLRA 127, 147, 148)
2 cm Muck (A10) (LRR N)
Stripped Matrix (S6)
Iron-Manganese Masses (F12) (LRR N,Other (Explain in Remarks)
3Indicators of hydrophytic vegetation and
wetland hydrology must be present,
Umbric Surface (F13) (MLRA 122, 136)
Piedmont Floodplain Soils (F19) (MLRA 148)
Sandy Gleyed Matrix (S4)MLRA 136)
Depleted Below Dark Surface (A11)
Thick Dark Surface (A12)
Sandy Mucky Mineral (S1)
Sandy Redox (S5)
% Texture
W1-UpSOIL
Type1
Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.)
Redox FeaturesDepth
(inches) Color (moist)Remarks
1Type: C=Concentration, D=Depletion, RM=Reduced Matrix, MS=Masked Sand Grains.2Location: PL=Pore Lining, M=Matrix.
%
Matrix
10YR 5/40-20
Loc2
Loamy/Clayey100
Color (moist)
Sampling Point:
Yes
Restrictive Layer (if observed):
Remarks:
Soils consistent with upland soils.
Hydric Soil Present?
Type:
Histosol (A1)
Histic Epipedon (A2)
Black Histic (A3)
Hydrogen Sulfide (A4)
Stratified Layers (A5)
ENG FORM 6116-4-SG, JUL 2018 Eastern Mountains and Piedmont – Version 2.0
Project/Site:Sampling Date:
Applicant/Owner:State:Sampling Point:
Investigator(s):
Landform (hillside, terrace, etc.):
Subregion (LRR or MLRA): Lat: Long:
Soil Map Unit Name:
X
Are Vegetation , Soil , or Hydrology Yes X
Are Vegetation , Soil , or Hydrology
SUMMARY OF FINDINGS – Attach site map showing sampling point locations, transects, important features, etc.
X No
X No X
X No
X X
X
X
X
Yes X
Yes X
Yes X X
U.S. Army Corps of Engineers
WETLAND DETERMINATION DATA SHEET – Eastern Mountains and Piedmont Region
See ERDC/EL TR-07-24; the proponent agency is CECW-CO-R
OMB Control #: 0710-xxxx, Exp: Pending
Requirement Control Symbol EXEMPT:
(Authority: AR 335-15, paragraph 5-2a)
Microtopographic Relief (D4)
FAC-Neutral Test (D5)
Inundation Visible on Aerial Imagery (B7)
Water-Stained Leaves (B9)
Aquatic Fauna (B13)
Algal Mat or Crust (B4)
Wetland Hydrology Present?
Stunted or Stressed Plants (D1)
NoYes
No
No
Water Table Present?
Primary Indicators (minimum of one is required; check all that apply) Surface Soil Cracks (B6)
Sparsely Vegetated Concave Surface (B8)
Drainage Patterns (B10)
Moss Trim Lines (B16)
Dry-Season Water Table (C2)
Crayfish Burrows (C8)
Surface Water (A1)
High Water Table (A2)
Saturation (A3)
Water Marks (B1)
Wetland Hydrology Indicators:
True Aquatic Plants (B14)
Saturation Visible on Aerial Imagery (C9)
Secondary Indicators (minimum of two required)
Wetland 1 is a floodplain wetland existing in the floodplain of S3. Thin layer of unconsolidated sand was observed covering entire wetland area. Due
to presence of hydrology indicators, hydrophytic vegetation, and hydric soils, sample point Wetland 1 is considered to be a wetland.
HYDROLOGY
Geomorphic Position (D2)
Shallow Aquitard (D3)
Hydrogen Sulfide Odor (C1)
Oxidized Rhizospheres on Living Roots (C3)
Presence of Reduced Iron (C4)
Recent Iron Reduction in Tilled Soils (C6)
Thin Muck Surface (C7)
Other (Explain in Remarks)
Iron Deposits (B5)
City/County:Willow Greenway and Upper McDowell Creek Restoration Cornelius / Mecklenburg
W1-Wet
10/24/18
Town of Cornelius NC
No
Section, Township, Range:Addie Lasitter
0ConcaveDepression
Datum: WGS84-80.86994435.470028LRR P, MLRA 136
NWI classification:MO
Slope (%):Local relief (concave, convex, none):
Yes NoAre climatic / hydrologic conditions on the site typical for this time of year?(If no, explain in Remarks.)
significantly disturbed?
naturally problematic?
Are “Normal Circumstances” present?
(If needed, explain any answers in Remarks.)
Remarks:

Is the Sampled AreaYes
Yes
Yes
Hydric Soil Present?
Hydrophytic Vegetation Present?
Wetland Hydrology Present?
Nowithin a Wetland? Yes
Saturation present throughout weltand area. Drainage patterns obsverved.
Sediment Deposits (B2)
Drift Deposits (B3)
Remarks:
Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available:
9
6
Depth (inches):
Depth (inches):
Depth (inches):
No
Saturation Present?
(includes capillary fringe)
Surface Water Present?
Field Observations:
ENG FORM 6116-4-SG, JUL 2018 Eastern Mountains and Piedmont – Version 2.0
Sampling Point:
(Plot size:
1.
2.
3.
4.
5.
6.(A/B)
7.
50% of total cover: 20% of total cover:x 1 =
Sapling/Shrub Stratum (Plot size:x 2 =
1.x 3 =
2.x 4 =
3.x 5 =
4.Column Totals:(B)
5.
6.
7.
8.X
9.X
4 - Morphological Adaptations1 (Provide supporting
50% of total cover: 20% of total cover:
Herb Stratum (Plot size:
1.
2.
3.
4.
5.
6.
7.
8.
9.
10.
11.
50% of total cover: 20% of total cover:
Woody Vine Stratum (Plot size:
1.
2.
3.
4.
5.
50% of total cover: 20% of total cover:Yes X
=Total Cover
Remarks: (Include photo numbers here or on a separate sheet.)
)5
=Total Cover
FACWYes
1 - Rapid Test for Hydrophytic Vegetation
2 - Dominance Test is >50%
VEGETATION (Four Strata)– Use scientific names of plants.
10 4 0
Yes FAC
90
0
0
Multiply by:
40
2.60Prevalence Index = B/A =
20
Yes FACW
Prevalence Index worksheet:
Total % Cover of:
30
0
(A)
(B)
(A)
2
410
5
15
Definitions of Four Vegetation Strata:
Woody Vine – All woody vines greater than 3.28 ft in
height.
Hydrophytic
Vegetation
Present?
=Total Cover
Herb – All herbaceous (non-woody) plants, regardless
of size, and woody plants less than 3.28 ft tall.
30 )
10
10
Cornus amomum
Arundinaria gigantea 10
20
Acer negundo
Tree Stratum
)
=Total Cover
Acer negundo
30 )
20
Indicator
Status
20
Dominant
Species?
Yes
10
FAC
OBL species
FACW species
FAC species
Sapling/Shrub – Woody plants, excluding vines, less
than 3 in. DBH and greater than or equal to 3.28 ft
(1 m) tall.
Tree – Woody plants, excluding vines, 3 in. (7.6 cm) or
more in diameter at breast height (DBH), regardless of
height.
1Indicators of hydric soil and wetland hydrology must be
present, unless disturbed or problematic.
Absolute
% Cover
100.0%
Percent of Dominant Species
That Are OBL, FACW, or FAC:
3 - Prevalence Index is ≤3.01
data in Remarks or on a separate sheet)
Problematic Hydrophytic Vegetation1 (Explain)
No
W1-Wet
4
4
FACU species
UPL species
Hydrophytic Vegetation Indicators:
0
130
0
50
Total Number of Dominant
Species Across All Strata:
Dominance Test worksheet:
Number of Dominant Species
That Are OBL, FACW, or FAC:
ENG FORM 6116-4-SG, JUL 2018 Eastern Mountains and Piedmont – Version 2.0
X
X
Depth (inches):X
Sampling Point:
Yes
Restrictive Layer (if observed):
Remarks:
Thin layer of unconsolidated sand present at sample point.
Hydric Soil Present?
Type:
Histosol (A1)
Histic Epipedon (A2)
Black Histic (A3)
Hydrogen Sulfide (A4)
Stratified Layers (A5)
Loc2
92
Loamy/Clayey
Loamy/Clayey
100
Color (moist)
Matrix
C10YR 4/2
10YR 3/3
7.5R 4/62-20
0-2
W1-WetSOIL
Type1
Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.)
Redox FeaturesDepth
(inches) Color (moist)Remarks
1Type: C=Concentration, D=Depletion, RM=Reduced Matrix, MS=Masked Sand Grains.2Location: PL=Pore Lining, M=Matrix.
%
Depleted Below Dark Surface (A11)
Thick Dark Surface (A12)
Sandy Mucky Mineral (S1)
Sandy Redox (S5)
%
M8
Sand present
Texture
Prominent redox concentrations
Stripped Matrix (S6)
Iron-Manganese Masses (F12) (LRR N,Other (Explain in Remarks)
3Indicators of hydrophytic vegetation and
wetland hydrology must be present,
Umbric Surface (F13) (MLRA 122, 136)
Piedmont Floodplain Soils (F19) (MLRA 148)
Sandy Gleyed Matrix (S4)MLRA 136)
Dark Surface (S7)unless disturbed or problematic.Red Parent Material (F21) (MLRA 127, 147, 148)
No
Hydric Soil Indicators:
Polyvalue Below Surface (S8) (MLRA 147, 148)
Thin Dark Surface (S9) (MLRA 147, 148)
Loamy Gleyed Matrix (F2)
Redox Dark Surface (F6)
Redox Depressions (F8)
Loamy Mucky Mineral (F1) (MLRA 136)
Depleted Matrix (F3)
Depleted Dark Surface (F7)
2 cm Muck (A10) (MLRA 147)
Coast Prairie Redox (A16)
Indicators for Problematic Hydric Soils3:
(MLRA 147, 148)
Piedmont Floodplain Soils (F19)
(MLRA 136, 147)
Very Shallow Dark Surface (F22)
Red Parent Material (F21)
(outside MLRA 127, 147, 148)
2 cm Muck (A10) (LRR N)
ENG FORM 6116-4-SG, JUL 2018 Eastern Mountains and Piedmont – Version 2.0
MORPHOLOGICAL DATA
Willow Pond Stream Rehabilitation
Min Max Min Max Min Max Min Max
1 Stream Type (Rosgen)
2 Drainage Area (square miles)
3 Bankfull Width (Wbkf)
4 Bankfull Mean Depth (dbkf)
5 Width/Depth Ratio (Wbkf/dbkf)
6 Bankfull Cross-Sectional Area (Abkf)
7 Bankfull Mean Velocity, ft/s (Vbkf)
8 Bankfull Maximum Depth (dmax)
9 Max dmax/dbkf ratio
10 Low Bank Height to Max Bankfull dbkf ratio
11 Entrenchment Ratio (Wfpa/Wbkf)
12 Ratio of Meander Length to Bankfull Width (Lm/Wbkf)
13 Ratio of Radius of Curvature to Bankfull Width (Rc/Wbkf)
14 Belt Width Ratio (Wblt/Wbkf)
15 Sinuosity (k) (Stream Length / Valley Length)
16 Ratio of Pool Depth to Bkf Depth (Dpool/dbkf)
17 Ratio of Pool to Pool Spacing to Bankfull Width (p-p/Wbkf)
1 Historically straightened and ditched channel. Most of the observed reaches were highly degraded and lacked defined riffle and pool features.
2 Proposed minor pattern adjustments only.
2.5 2.5--
--
--
--
3.4
23.4
--
Willow Pond
McDowell
DESIGN
1.1
3.5
22.4
1.8
B
1.0
2.8
0.9
11.3
3.3
--
--
1.7
2.6
1.3
1.4
2.1
5.5
--
--
--
1.9
1.1 0.6
3.0 1.0
VARIABLES
(All units are in Feet)
21.04.1
0.2
Willow Pond
McDowell
EXISTING
20.8
B
0.9
1.0 3.2
2.0
1.06 1.06
18.9
B
Mecklenburg County, North Carolina
----
1.21.3
7.84.2
2.5
--
7.1 3.8
Willow Pond
Tributary
EXISTING
Willow Pond
Tributary
DESIGN
B
0.2
4.4 12.6
--
1.2 2.0
1.09 1.09
2.2

North Carolina Department of Natural and Cultural Resources
State Historic Preservation Office
Ramona M. Bartos, Administrator
Governor Roy Cooper Office of Archives and History
Secretary Susi H. Hamilton Deputy Secretary Kevin Cherry
Location: 109 East Jones Street, Raleigh NC 27601 Mailing Address: 4617 Mail Service Center, Raleigh NC 27699-4617 Telephone/Fax: [phone]-6599

August 16, 2018

Adrienne Lassiter
Kimley-Horn and Associates, Inc.
200 South Tryon Street, Suite 200
Charlotte, NC 28203

Re: Cornelius Greenway & Willow Pond Stream Restoration, Westmoreland Road and East Catawba
Avenue, Cornelius, EB-5777, Mecklenburg County, ER 18-1639

Dear Ms. Lassiter:
Thank you for your letter of July 17, 2018, concerning the above project.
We have conducted a review of the project and are aware of no historic resources which would be affected by
the project. Therefore, we have no comment on the project as proposed.

The above comments are made pursuant to Section 106 of the National Historic Preservation Act and the
Advisory Council on Historic Preservation’s Regulations for Compliance with Section 106 codified at 36 CFR
Part 800.

Thank you for your cooperation and consideration. If you have questions concerning the above comment,
contact Renee Gledhill-Earley, environmental review coordinator, at 919-807-6579 or
[e-mail]. In all future communication concerning this project, please cite the above
referenced tracking number.
Sincerely,

Ramona M. Bartos

7/17/2018
IPaC
IPaC: Explore Location
U.S. Fish & Wildlife Service
IPaC resource list
Last login July 09, 2018 01:48 PM MDT
This report is an automatically generated list of species and other resources such as critical habitat
(collectively referred to as trust resources) under the U.S. Fish and Wildlife Service's (USFWS)
jurisdiction that are known or expected to be on or near the project area referenced below. The list
may also include trust resources that occur outside of the project area, but that could potentially be
directly or indirectly affected by activities in the project area. However, determining the likelihood
and extent of effects a project may have on trust resources typically requires gathering additional
site -specific (e.g., vegetation/species surveys) and project -specific (e.g., magnitude and timing of
proposed activities) information.
Below is a summary of the project information you provided and contact information for the USFWS
office(s) with jurisdiction in the defined project area. Please read the introduction to each section
that follows (Endangered Species, Migratory Birds, USFWS Facilities, and NWI Wetlands) for
additional information applicable to the trust resources addressed in that section.
Location
Mecklenburg County, North Carolina
.IG.-0
C
i. -ill�Iirls .
_ I
Local office
Asheville Ecological Services Field Office
L [phone]
18 [phone]
160 Zillicoa Street
Asheville, NC 28801-1082
http://www.fws.gov/nc-es/es/countyfr.html
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7/17/2018 IPaC: Explore Location
Endangered species
This resource list is for informational purposes only and does not constitute an analysis of
project level impacts.
The primary information used to generate this list is the known or expected range of each species.
Additional areas of influence (AOI) for species are also considered. An AOI includes areas outside of
the species range if the species could be indirectly affected by activities in that area (e.g., placing a
dam upstream of a fish population, even if that fish does not occur at the dam site, may indirectly
impact the species by reducing or eliminating water flow downstream). Because species can move,
and site conditions can change, the species on this list are not guaranteed to be found on or near
the project area. To fully determine any potential effects to species, additional site -specific and;
project -specific information is often required. \A
Section 7 of the Endangered Species Act requires Federal agencies to "request of the Secretary
information whether any species which is listed or proposed to be listed may be present in the area
of such proposed action" for any project that is conducted, permitted, funded, or licensed by any
Federal agency. A letter from the local office and a species list which fulfills this requirement can
only be obtained by requesting an official species list from either the Regulatory Review section in
IPaC (see directions below) or from the local field office directly.
For project evaluations that require USFWS concurrence/review, please return to the IPaC website
and request an official species list by doing the following:
1. Draw the project location and click CONTINUE.
2. Click DEFINE PROJECT.
3. Log in (if directed to do so):..
4. Provide a name and description for your project.
5. Click REQUEST SPECIES LIST.
Listed speciesl and their critical habitats are managed by the Ecological Services Program of the U.S.
Fish and Wildlife Service (USFWS) and the fisheries division of the National Oceanic and Atmospheric
Administration (NOAA Fisheries2).
Species and critical habitats under the sole responsibility of NOAA Fisheries are not shown an this
list. Please contact NOAA Fisheries for species under their jurisdiction.
1. Species listed under the Endangered Species Act are threatened or endangered; IPaC also shows
species that are candidates, or proposed, for listing. See the listing status page for more
information.
2. NOAA Fisheries, also known as the National Marine Fisheries Service (NMFS), is an office of the
National Oceanic and Atmospheric Administration within the Department of Commerce.
The following species are potentially affected by activities in this location:
Mammals
NAME STATUS
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Northern Long-eared Bat Myotis septentrionalis Threatened
No critical habitat has been designated for this species.
https://ecos.fws.gov/ecp/species/9045
Clams
NAME STATUS
Carolina Heelsplitter Lasmigona decorata Endangered
There is final critical habitat for this species. Your location is outside
the critical habitat.
https://ecos.fws.gov/ecp/species/3534
Flowering Plants
NAME
Michaux's Sumac Rhus michauxii
No critical habitat has been designated for this species.
httpa //eco s. fws.gav/ec p/speci es/5217
STATUS
Endangere
Schweinitz's Sunflower Helianthus schweinitzii Endangered
No critical habitat has been designated for this species.
httpL.//ecos.fws.gov/ecp speci es/3849
Smooth Coneflower Echinacea laevigata Endangered
IN critical habitat has been designated for this species.
httpsWecos.fws.gov/ecplspecies/3473
Critical habitats
Potential effects to critical habitat(s) in this location must be analyzed along with the endangered
species themselves.
THERE ARE NO CRITICAL HABITATS AT THIS LOCATION.
Migratory birds
Certain birds are protected under the Migratory Bird Treaty Act! and the Bald and Golden Eagle
Protection Acts.
Any person or organization who plans or conducts activities that may result in impacts to migratory
birds, eagles, and their habitats should follow appropriate regulations and consider implementing
appropriate conservation measures, as described below.
1. The Migratory Birds Treaty Act of 1918.
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7/17/2018 IPaC: Explore Location
2. The Bald and Golden Eagle Protection Act of 1940.
Additional information can be found using the following links:
Birds of Conservation Concern http://www.fws.gov/birds/management/managed-species/
birds-of-conservation-concern.php
Measures for avoiding and minimizing impacts to birds
http://www.fws.gov/birds/management/project-assessment-tools-and-guidance/
conservation-measures.php
Nationwide conservation measures for birds
http://www.fws.gov/migratorybirds/pdf/management/nationwidestandardconservationmeasures.pdf
The birds listed below are birds of particular concern either because they occur on the USFWS Birds
of Conservation Concern (BCC) list or warrant special attention in your project location. To learn
more about the levels of concern for birds on your list and how this list is generated, see the FAQ
below. This is not a list of every bird you may find in this location, nor a guarantee that every bird on
this list will be found in your project area. To see exact locations of where birders and the general
public have sighted birds in and around your project area, visit the E-bird data mapping tool (Tip:
enter your location, desired date range and a species on your list). For projects that occur off the
Atlantic Coast, additional maps and models detailing the relative occurrence and abundance of bird
species on your list are available. Links to additional information about Atlantic Coast birds, and
other important information about your migratory bird list, including how to properly interpret and
use your migratory bird report, can be found below.,`
For guidance on when to schedule activities or implement avoidance and minimization measures to
reduce impacts to migratory birds on your list, click on the PROBABILITY OF PRESENCE SUMMARY at
the top of your list to see when these birds are most likely to be present and breeding in your
project area.
NAME
�o�
Bald Eagle Haliaeetus leucocephalus
This is not a Bird of Conservation Concern (BCC) in this area, but
warrants attention because of the Eagle Act or for potential
susceptibilities in offshore areas from certain types of development
or activities.
https://ecos.fws.gov/ecp/species/1626
BREEDING SEASON (IF A
.. ... ... ... .. ..
BREEDING SEASON IS INDICATED
FOR A BIRD ON YOUR LIST, THE
.. ... ... ... .. ........ .
BIRD MAY BREED IN YOUR
PROJECT AREA SOMETIME WITHIN
...............................................................................11
THE TIMEFRAME SPECIFIED,
.........................................................................................
WHICH IS A VERY LIBERAL
ESTIMATE OF THE DATES INSIDE
_.......................................................................................................
WHICH THE BIRD BREEDS
ACROSS ITS ENTIRE RANGE.
"BREEDS ELSEWHERE" INDICATES
.............................................................................................................
THATTHE BIRD DOES NOT LIKELY
............................................................................................................
BREED IN YOUR PROJECT AREA.)
........................................................................................................
Breeds Sep 1 to Jul 31
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7/17/2018
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Blue -winged Warbler Vermivora pinus
This is a Bird of Conservation Concern (BCC) only in particular Bird
Conservation Regions (BCRs) in the continental USA
Eastern Whip -poor -will Antrostomus vociferus
This is a Bird of Conservation Concern (BCC) throughout its range in
the continental USA and Alaska.
Prairie Warbler Dendroica discolor
This is a Bird of Conservation Concern (BCC) throughout its range in
the continental USA and Alaska.
Red-headed Woodpecker Melanerpes erythrocephalus
This is a Bird of Conservation Concern (BCC) throughout its range in
the continental USA and Alaska.
Rusty Blackbird Euphagus carolinus
This is a Bird of Conservation Concern (BCC) throughout its range in
Breeds May 1 to Jun 30
Breeds May 1 to Aug 20
Breeds May 1 to Jul 31
Breeds May 10 to Sep 10
Breeds elsewhere
the contlnental USA and Alaska.
Wood Thrush Hylobchla mustefina Breeds May 10 to Aug 31
This is a Bird of Conservation Concern (BCC) throughout its range in
the continental USA and Alaska.
Probability of Presence Summary
The graphs below provide our best understanding of when birds of concern are most likely to be
present in your project area. This information can be used to tailor and schedule your project
activities to avoid or minimize impacts to birds. Please make sure you read and understand the FAQ
"Proper Interpretation and Use of Your Migratory Bird Report" before using or attempting to
interpret this report.
Probability of Presence ( )
Each green bar represents the bird's relative probability of presence in the 10km grid cells) your
project overlaps during a particular week of the year. (A year is represented as 12 4-week months.)
A taller bar indicates a higher probability of species presence. The survey effort (see below) can be
used to establish a level of confidence in the presence score. One can have higher confidence in the
presence score if the corresponding survey effort is also high.
How is the probability of presence score calculated? The calculation is done in three steps:
1. The probability of presence for each week is calculated as the number of survey events in the
week where the species was detected divided by the total number of survey events for that
week. For example, if in week 12 there were 20 survey events and the Spotted Towhee was
found in 5 of them, the probability of presence of the Spotted Towhee in week 12 is 0.25.
2. To properly present the pattern of presence across the year, the relative probability of presence
is calculated. This is the probability of presence divided by the maximum probability of presence
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IPaC: Explore Location
across all weeks. For example, imagine the probability of presence in week 20 for the Spotted
Towhee is 0.05, and that the probability of presence at week 12 (0.25) is the maximum of any
week of the year. The relative probability of presence on week 12 is 0.25/0.25 = 1; at week 20 it is
0.05/0.25 = 0.2.
3. The relative probability of presence calculated in the previous step undergoes a statistical
conversion so that all possible values fall between 0 and 10, inclusive. This is the probability of
presence score.
To see a bar's probability of presence score, simply hover your mouse cursor over the bar.
Breeding Season( )
Yellow bars denote a very liberal estimate of the time -frame inside which the bird breeds across its
entire range. If there are no yellow bars shown for a bird, it does not breed in your project area.
Survey Effort (1)
Vertical black lines superimposed on probability of presence bars indicate the number of surveys
performed for that species in the 10km grid cell(s) your project area overlaps. The number of
surveys is expressed as a range, for example, 33 to 54 surveys.
To see a bar's survey effort range, simply hover your mouse cursor over the bar.A
No Data (—)
A week is marked as having no data if there were no survey events for that week.
Survey Timeframe
Surveys from only the last 10 years are used in order to ensure delivery of currently relevant
information. The exception to this is areas off the Atlantic coast, where bird returns are based on all
years of available data, since data in these areas is currently much more sparse.
SPECIES
Bald Eagle
Non -BCC Vulnerable
..................................................
(This is not a Bird of
Conservation
................................
Concern (BCC] in this
..................................................
area, but warrants
.............................................
attention because of
the Eagle Act or for
potential
......................
susceptibilities in
offshore areas from
.................................................
certain types of
......................................
development or
......................................
activities.)
Blue -winged
Warbler
BCC - BCR (This is a
...............................................
Bird of Conservation
..................................................
Concern (BCC) only in
.....................................................
particular Bird
...........
Conservation Regions
(BCRs) in the
...............................
continental USA)
.. probability of presence breeding season I survey effort — no data
]AN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC
a
4-1 I I 1 1 11 1 1 1 1 1 1 1 1 1 1 1 E 1 1 1 1 -- _1,Fill Jill 1. 1 1 ' 1 1 1
1-+++ ++++ ++++ +++I I I I I I I I I _-_- --+- +1++ ++++ +-++ -+-11
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Eastern Whip
IPaC: Explore Location
poor -will
BCC Rangewide
(CON) (This is a Bird
of Conservation
.......................................
Concern (BCC)
...................................
throughout its range
in the continental
...........................................
USA and Alaska.)
Prairie Warbler
BCC Rangewide
(CON) (This is a Bird
of Conservation
.......................................
Concern (BCC)
throughout its range
in the continental
...........................................
USA and Alaska.)
.........................................
Red-headed
Woodpecker
BCC Rangewide
(CON) (This is a Bird
of Conservation
Co
......................................
ncern (BCC)
.... ...............................
throughout its range
in the continental
...........................................
USA and Alaska.)
Rusty Blackbird
BCC Rangewide
......................................
(CON) (This is a Bird
.. ..............................................
of Conservation
............................. .....
Concern (BCC)
throughout its range
..................................................
in the continental
...........................................
USA and Alaska.)
Woad Thrush
BCC Rangewide
(CON) (This is a Bird
...............................................
of Conservation
......................................
Concern (BC C)
...................................
throughout its.range
in the continental
...........................................
USA and Alaska.)
.........................................
+ j++ i"' IN-
++++ +++-- +-++ -+++
++++
++++ ++++ ++IN I I I I I I I I I I I I --+- ++++ ++++ +-++ -+++
�+-4-. +1$1 ++++ ++++ *�111111 Illy I��11�+� ���� 4-- +
1114
0
I-+++ ++++ +1++ ++++ ++.+ ++++ -- ++ a +++ + �++ • J+ +
i
++++ ++++ +++ ++-F+ ,'++ ++++ —+++
Tell me more about conservation measures I can implement to avoid or minimize Impacts to migratory birds.
Nationwide Conservation Measures describes measures that Can help avoid and minimize Impacts to all birds at
any location year round. Implementation of these measures is particularly important when birds are most likely to
occur in the project area. When birds may be breeding in the area, identifying the locations of any active nests and
avoiding their destruction is a very helpful impact minimization measure. To see when birds are most likely to
occur and be breeding in your project area, view the Probability of Presence Summary. Additional measures and/or
permits may be advisable depending on the type of activity you are conducting and the type of infrastructure or
bird species present on your project site.
What does IPaC use to generate the migratory birds potentially occurring in my specified location?
The Migratory Bird Resource List is comprised of USFWS Birds of Conservation Concern (BCC) and other species
that may warrant special attention in your project location.
The migratory bird list generated for your project is derived from data provided by the Avian Knowledge Network
(AKN). The AKN data is based on a growing collection of survey, banding, and citizen science datasets and is
queried and filtered to return a list of those birds reported as occurring in the 10km grid cell(s) which your project
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intersects, and that have been identified as warranting special attention because they are a BCC species in that
area, an eagle (Eagle Act requirements may apply), or a species that has a particular vulnerability to offshore
activities or development.
Again, the Migratory Bird Resource list includes only a subset of birds that may occur in your project area. It is not
representative of all birds that may occur in your project area. To get a list of all birds potentially present in your
project area, please visit the E-bird Explore Data Tool.
What does IPaC use to generate the probability of presence graphs for the migratory birds potentially
occurring in my specified location?
The probability of presence graphs associated with your migratory bird list are based on data provided by the
Avian Knowledge Network (AKN). This data is derived from a growing collection of survey,, banding, and citizen
science datasets .
Probability of presence data is continuously being updated as new and better information becomes available. To
learn more about how the probability of presence graphs are produced and how to interpret them, g6the
Probability of Presence Summary and then click on the "Tell me about these graphs" link.
4
How do I know if a bird is breeding, wintering, migrating or present year-round in my project area?
To see what part of a particular bird's range your project area falls within (i.e. breeding, wintering, migrating or
year-round), you may refer to the following resources: The Cornell Lab of Ornithology All About Birds Bird Guide, or
(if you are unsuccessful in locating the bird of interest there), the Cornell Lab of Ornithology NeotropicaI Birds
guide. If a bird on your migratory bird species list has a breeding season associated with it, if that bird does occur
in your project area, there may be nests present at some point within the timeframe specified. If "Breeds
elsewhere" is indicated, then the bird likely does not breed in your project area.
What are the levels of concern for migratory birds? .01
Migratory birds delivered through IPaC fall into the following distinct categories of concern:
1. "BCC Rangewide" birds are Birds of Conservation Concern (BCC) that are of concern throughout their range
anywhere within the USA (including Hawaii, the Pacific Islands, Puerto Rico, and the Virgin Islands);
2. "BCC - BCR" birds are BCCs that are of concern only in particular Bird Conservation Regions (BCRs) in the
continental USA; and
3. "Non -BCC - Vulnerable" birds are not BCC species in your project area, but appear on your list either because of
the Eagle Act requirements (for eagles) or (for non -eagles) potential susceptibilities in offshore areas from
certain types of development or activities (e.g. offshore energy development or longline fishing).
Although it is important to try to avoid and minimize impacts to all birds, efforts should be made, in particular, to
avoid and minimize impacts to the birds on this list, especially eagles and BCC species of rangewide concern. For
more information on conservation measures you can implement to help avoid and minimize migratory bird
impacts and requirements for eagles, please see the FAQs for these topics.
Details about birds that are potentially affected by offshore projects
For additional details about the relative occurrence and abundance of both individual bird species and groups of
bird species within your project area off the Atlantic Coast, please visit the Northeast Ocean Data Portal. The Portal
also offers data and information about other taxa besides birds that may be helpful to you in your project review.
Alternately, you may download the bird model results files underlying the portal maps through the NOAA NCCOS
Integrative Statistical Modeling and Predictive Mapping of Marine Bird Distributions and Abundance on the Atlantic
Outer Continental Shelf project webpage.
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Bird tracking data can also provide additional details about occurrence and habitat use throughout the year,
including migration. Models relying on survey data may not include this information. For additional information on
marine bird tracking data, see the Diving Bird Study and the nanotag studies or contact Caleb Spiegel or Pam
Loring.
What if I have eagles on my list?
If your project has the potential to disturb or kill eagles, you may need to obtain a permit to avoid violating the
Eagle Act should such impacts occur.
Proper Interpretation and Use of Your Migratory Bird Report
The migratory bird list generated is not a list of all birds in your project area, only a subset of birds of priority
concern. To learn more about how your list is generated, and see options for identifying what other birds may be
in your project area, please see the FAQ "What does IPaC use to generate the migratory birds potentially occurring
in my specified location". Please be aware this report provides the "probability of presence" of birds within the 10
km grid cell(s) that overlap your project; not your exact project footprint. On the graphs provided, please also look
carefully at the survey effort (indicated by the black vertical bar) and for the existence of the "no data" indicator (a
red horizontal bar). A high survey effort is the key component. If the survey effort is high, then the probability of
presence score can be viewed as more dependable. In contrast, a low survey effort bar or no data bar means a lack
of data and, therefore, a lack of certainty about presence of the species. This list is not perfect; it is simply a starting
point for identifying what birds of concern have the potential to be in your project area, when they might be there,
and if they might be breeding (which means nests might be present). The list helps you know what to look for to
confirm presence, and helps guide you in knowing when to implement conservation measures to avoid or
minimize potential impacts from your project activities, should presence be confirmed. To learn more about
conservation measures, visit the FAQ "Tell me about conservation measures I can implement to avoid or minimize
impacts to migratory birds" at the bottom of your migratory bird trust resources page.
Facilities
Wildlife refuges and fish hatcheries
REFUGE AND FISH HATCHERY INFORMATION IS NOT AVAILABLE AT THIS TIME
\4*44 %EP-
Wetlands in the National Wetlands Inventory
Impacts to NWI wetlands and other aquatic habitats may be subject to regulation under Section 404
of the Clean Water Act, or other State/Federal statutes.
For more information please contact the Regulatory Program of the local U.S. Army Corps of
Engineers District.
Please note that the NWI data being shown may be out of date. We are currently working to update
our NWI data set. We recommend you verify these results with a site visit to determine the actual
extent of wetlands on site.
This location overlaps the following wetlands:
https://ecos.fws.gov/ipac/location/AV6ZUA4WJVGSXLKYDSWTS7LAAM/resources 9/10

7/17/2018 IPaC: Explore Location
FRESHWATER FORESTED/SHRUB WETLAND
PF01A
FRESHWATER POND
PUBHh
RIVERINE
R2UBHx
R4SBC
A full description for each wetland code can be found at the National Wetlands Inventory website
Data limitations
The Service's objective of mapping wetlands and deepwater habitats is to produce reconnaissance level
information on the location, type and size of these resources. The maps are prepared from the analysis of high
altitude imagery. Wetlands are identified based on vegetation, visible hydrology and geography. A margin of error
is Inherent in the use of imagery; thus, detailed on -the -ground inspection of any particular site may result in
revision of the wetland boundaries or classification established through image analysis. 00% % NMO
The accuracy of image interpretation depends on the quality of the imagery, the experience of the image analysts,
the amount and quality of the collateral data and the amount of ground truth verification work conducted.
Metadata should be consulted to determine the date of the source imagery used and any mapping problems.
Wetlands or other mapped features may have changed since the date of the imagery or field work. There may be
occasional differences in polygon boundaries or classifications between the information depicted on the map and
the actual conditions on site.
Data exclusions
Certain wetland habitats are excluded from the'National mapping program because of the limitations of aerial
imagery as the primary data source used to detect wetlands. These habitats include seagrasses or submerged
aquatic vegetation that are found in the intertidal and subtidaI zones of estuaries and nearshore coastal waters.
Some deepwater reef communities (coral ❑rtuberficid warm reefs) have also been excluded from the inventory.
These habitats, because of their depth, go undetected by aerial imagery.
Data precautions
Federal, state, and local regulatory agencies with jurisdiction over wetlands may define and describe wetlands in a
different manner than that used in this inventory. There is no attempt, in either the design or products of this
inventory, to define the limits of proprietary jurisdiction of any Federal, state, or local government or to establish
the geographical scope of the regulatory programs of government agencies. Persons intending to engage in
activities involving modifications within or adjacent to wetland areas should seek the advice of appropriate federal,
state, or local agencies concerning specified agency regulatory programs and proprietary jurisdictions that may
affect such activities.
https://ecos.fws.gov/ipac/location/AV6ZUA4WJVGSXLKYDSWTS7LAAM/resources 10/10

NCNHDE-6482
July 17, 2018
Chris Tinklenberg
Kimley-Horn
200 South Tryon St.
Charlotte, NC 28202
RE: Cornelius Greenway and Willow Pond Stream Restoration (EB-5777)
Dear Chris Tinklenberg:
The North Carolina Natural Heritage Program (NCNHP) appreciates the opportunity to provide information
about natural heritage resources for the project referenced above.
A query of the NCNHP database indicates that there are records for rare species, important natural
communities, natural areas, and/or conservation/managed areas within the proposed project boundary. These
results are presented in the attached ‘Documented Occurrences’ tables and map.
The attached ‘Potential Occurrences’ table summarizes rare species and natural communities that have been
documented within a one-mile radius of the property boundary. The proximity of these records suggests that
these natural heritage elements may potentially be present in the project area if suitable habitat exists. Tables of
natural areas and conservation/managed areas within a one-mile radius of the project area, if any, are also
included in this report.
If a Federally-listed species is documented within the project area or indicated within a one-mile radius of the
project area, the NCNHP recommends contacting the US Fish and Wildlife Service (USFWS) for guidance.
Contact information for USFWS offices in North Carolina is found here:
https://www.fws.gov/offices/Directory/ListOffices.cfm?statecode=37.
Please note that natural heritage element data are maintained for the purposes of conservation planning, project
review, and scientific research, and are not intended for use as the primary criteria for regulatory decisions.
Information provided by the NCNHP database may not be published without prior written notification to the
NCNHP, and the NCNHP must be credited as an information source in these publications. Maps of NCNHP
data may not be redistributed without permission.
Also please note that the NC Natural Heritage Program may follow this letter with additional correspondence if a
Dedicated Nature Preserve, Registered Heritage Area, Clean Water Management Trust Fund easement, or an
occurrence of a Federally-listed species is documented near the project area.
If you have questions regarding the information provided in this letter or need additional assistance, please
contact Rodney A. Butler at [e-mail] or 919-707-8603.
Sincerely,
NC Natural Heritage Program
Natural Heritage Element Occurrences, Natural Areas, and Managed Areas Intersecting the Project Area
Cornelius Greenway and Willow Pond Stream Restoration (EB-5777)
July 17, 2018
NCNHDE-6482
No Element Occurrences are Documented within the Project Area
There are no documented element occurrences (of medium to very high accuracy) that intersect with the project area. Please note, however, that although the NCNHP database
does not show records for rare species within the project area, it does not necessarily mean that they are not present; it may simply mean that the area has not been surveyed. The
use of Natural Heritage Program data should not be substituted for actual field surveys if needed, particularly if the project area contains suitable habitat for rare species. If rare
species are found, the NCNHP would appreciate receiving this information so that we may update our database.
No Natural Areas are Documented within the Project Area
Managed Areas Documented Within Project Area*
Managed Area Name Owner Owner Type
Mecklenburg County Open Space Mecklenburg County Local Government
*NOTE: If the proposed project intersects with a conservation/managed area, please contact the landowner directly for additional information. If the project intersects with a Dedicated Nature Preserve (DNP), Registered Natural
Heritage Area (RHA), or Federally-listed species, NCNHP staff may provide additional correspondence regarding the project.
Definitions and an explanation of status designations and codes can be found at https://ncnhde.natureserve.org/content/help. Data query generated on July 17, 2018; source: NCNHP, Q2 April 2018. Please resubmit your
information request if more than one year elapses before project initiation as new information is continually added to the NCNHP database.
Page 2 of 4
Natural Heritage Element Occurrences, Natural Areas, and Managed Areas Within a One-mile Radius of the Project Area
Cornelius Greenway and Willow Pond Stream Restoration (EB-5777)
July 17, 2018
NCNHDE-6482
No Element Occurrences are Documented Within a One-mile Radius of the Project Area
No Natural Areas are Documented Within a One-mile Radius of the Project Area
Managed Areas Documented Within a One-mile Radius of the Project Area
Managed Area Name Owner Owner Type
NC Division of Mitigation Services Easement NC DEQ, Division of Mitigation Services State
Mecklenburg County Open Space Mecklenburg County Local Government
Town of Cornelius Open Space Town of Cornelius Local Government
Definitions and an explanation of status designations and codes can be found at https://ncnhde.natureserve.org/content/help. Data query generated on July 17, 2018; source: NCNHP, Q2 April 2018. Please resubmit your
information request if more than one year elapses before project initiation as new information is continually added to the NCNHP database.
Page 3 of 4
Powered by TCPDF (www.tcpdf.org)
Page 4 of 4
United States Department of the Interior
FISH AND WILDLIFE SERVICE
Asheville Ecological Services Field Office
160 Zillicoa Street
Asheville, NC 28801-1082
Phone: [phone] Fax: [phone]
http://www.fws.gov/nc-es/es/countyfr.html
In Reply Refer To:
Consultation Code: 04EN1000-2018-SLI-0586
Event Code: 04EN1000-2018-E-01573
Project Name: Willow Pond GW

Subject:List of threatened and endangered species that may occur in your proposed project
location, and/or may be affected by your proposed project
To Whom It May Concern:
The attached species list identifies threatened, endangered, proposed and candidate species, as
well as proposed and final designated critical habitat, that may occur within the boundary of your
proposed project and/or may be affected by your proposed project. Although not required by
section 7, many agencies request species lists to start the informal consultation process and begin
their fulfillment of the requirements under section 7(c) of the Endangered Species Act (Act) of
1973, as amended (16 U.S.C. 1531 et seq.).
This list, along with other helpful resources, is also available on the U.S. Fish and Wildlife
Service (Service) Asheville Field Office's (AFO) website: https://www.fws.gov/raleigh/species/
cntylist/nc_counties.html. The AFO website list includes “species of concern” species that could
potentially be placed on the federal list of threatened and endangered species in the future. Also
available are:
Design and Construction Recommendations
https://www.fws.gov/asheville/htmls/project_review/Recommendations.html
Optimal Survey Times for Federally Listed Plants
https://www.fws.gov/nc-es/plant/plant_survey.html
Northern long-eared bat Guidance
https://www.fws.gov/asheville/htmls/project_review/NLEB_in_WNC.html
Predictive Habitat Model for Aquatic Species
https://www.fws.gov/asheville/htmls/Maxent/Maxent.html
July 17, 2018
07/17/2018 Event Code: 04EN1000-2018-E-01573   2

New information based on updated surveys, changes in the abundance and distribution of
species, changed habitat conditions, or other factors could require modifications of these lists.
Please note that under 50 CFR 402.12(e) of the regulations implementing section 7 of the Act,
the accuracy of the species lists should be verified after 90 days. This verification can be
completed formally or informally as desired. The Service recommends that verification be
completed by visiting the ECOS-IPaC website or the AFO website (the AFO website dates each
county list with the day of the most recent update/change) at regular intervals during project
planning and implementation for updates to species lists and information. An updated list may be
requested through the ECOS-IPaC system by completing the same process used to receive the
enclosed list or by going to the AFO website.
The purpose of the Act is to provide a means whereby threatened and endangered species and the
ecosystems upon which they depend may be conserved. Under sections 7(a)(1) and 7(a)(2) of the
Act and its implementing regulations (50 CFR 402 et seq.), Federal agencies are required to
utilize their authorities to carry out programs for the conservation of threatened and endangered
species and to determine whether projects may affect threatened and endangered species and/or
designated critical habitat.
A Biological Assessment is required for construction projects (or other undertakings having
similar physical impacts) that are major Federal actions significantly affecting the quality of the
human environment as defined in the National Environmental Policy Act (42 U.S.C. 4332(2)
(c)). For projects other than major construction activities, the Service suggests that a Biological
Evaluation similar to a Biological Assessment be prepared to determine whether the project may
affect listed or proposed species and/or designated or proposed critical habitat. Recommended
contents of a Biological Assessment are described at 50 CFR 402.12 and on our office's website
at https://www.fws.gov/asheville/htmls/project_review/assessment_guidance.html.
If a Federal agency (or their non-federal representative) determines, based on the Biological
Assessment or Biological Evaluation, that listed species and/or designated critical habitat may be
affected by the proposed project, the agency is required to consult with the Service pursuant to
50 CFR 402. In addition, the Service recommends that candidate species, proposed species, and
proposed critical habitat be addressed within the consultation. More information on the
regulations and procedures for section 7 consultation, including the role of permit or license
applicants, can be found in the "Endangered Species Consultation Handbook" at: http://
www.fws.gov/endangered/esa-library/pdf/TOC-GLOS.PDF.
Though the bald eagle is no longer protected under the Endangered Species Act, please be aware
that bald and golden eagles are protected under the Bald and Golden Eagle Protection Act (16
U.S.C. 668 et seq.), and projects affecting these species may require additional consultation (see
https://www.fws.gov/southeast/our-services/permits/eagles/). Wind energy projects should follow
the wind energy guidelines (http://www.fws.gov/windenergy/) for minimizing impacts to
migratory birds (including bald and golden eagles) and bats.
Guidance for minimizing impacts to migratory birds for projects including communications
towers (e.g., cellular, digital television, radio, and emergency broadcast) can be found at: http://
07/17/2018 Event Code: 04EN1000-2018-E-01573   3

www.fws.gov/migratorybirds/CurrentBirdIssues/Hazards/towers/towers.htm;
http://www.towerkill.com; and http://www.fws.gov/migratorybirds/CurrentBirdIssues/Hazards/
towers/comtow.html.
We appreciate your concern for threatened and endangered species. The Service encourages
Federal agencies to include conservation of threatened and endangered species into their project
planning to further the purposes of the Act. Please include the Consultation Tracking Number in
the header of this letter with any request for consultation or correspondence about your project
that you submit to our office.
Attachment(s):
▪Official Species List
▪Migratory Birds
▪Wetlands
07/17/2018 Event Code: 04EN1000-2018-E-01573   1

Official Species List
This list is provided pursuant to Section 7 of the Endangered Species Act, and fulfills the
requirement for Federal agencies to "request of the Secretary of the Interior information whether
any species which is listed or proposed to be listed may be present in the area of a proposed
action".
This species list is provided by:
Asheville Ecological Services Field Office
160 Zillicoa Street
Asheville, NC 28801-1082
[phone]
07/17/2018 Event Code: 04EN1000-2018-E-01573   2

Project Summary
Consultation Code:04EN1000-2018-SLI-0586
Event Code:04EN1000-2018-E-01573
Project Name:Willow Pond GW
Project Type:RECREATION CONSTRUCTION / MAINTENANCE
Project Description:Greenway project
Project Location:
Approximate location of the project can be viewed in Google Maps: https://
www.google.com/maps/place/35.47341725925942N80.87304621995361W
Counties:Mecklenburg, NC
07/17/2018 Event Code: 04EN1000-2018-E-01573   3

Endangered Species Act Species
There is a total of 5 threatened, endangered, or candidate species on this species list.
Species on this list should be considered in an effects analysis for your project and could include
species that exist in another geographic area. For example, certain fish may appear on the species
list because a project could affect downstream species.
IPaC does not display listed species or critical habitats under the sole jurisdiction of NOAA
Fisheries , as USFWS does not have the authority to speak on behalf of NOAA and the
Department of Commerce.
See the "Critical habitats" section below for those critical habitats that lie wholly or partially
within your project area under this office's jurisdiction. Please contact the designated FWS office
if you have questions.
1.NOAA Fisheries, also known as the National Marine Fisheries Service (NMFS), is an
office of the National Oceanic and Atmospheric Administration within the Department of
Commerce.
Mammals
NAME STATUS
Northern Long-eared Bat Myotis septentrionalis
No critical habitat has been designated for this species.
Species profile: https://ecos.fws.gov/ecp/species/9045
Threatened
Clams
NAME STATUS
Carolina Heelsplitter Lasmigona decorata
There is final critical habitat for this species. Your location is outside the critical habitat.
Species profile: https://ecos.fws.gov/ecp/species/3534
Endangered
1
07/17/2018 Event Code: 04EN1000-2018-E-01573   4

Flowering Plants
NAME STATUS
Michaux's Sumac Rhus michauxii
No critical habitat has been designated for this species.
Species profile: https://ecos.fws.gov/ecp/species/5217
Endangered
Schweinitz's Sunflower Helianthus schweinitzii
No critical habitat has been designated for this species.
Species profile: https://ecos.fws.gov/ecp/species/3849
Endangered
Smooth Coneflower Echinacea laevigata
No critical habitat has been designated for this species.
Species profile: https://ecos.fws.gov/ecp/species/3473
Endangered
Critical habitats
THERE ARE NO CRITICAL HABITATS WITHIN YOUR PROJECT AREA UNDER THIS OFFICE'S
JURISDICTION.
07/17/2018 Event Code: 04EN1000-2018-E-01573   1

Migratory Birds
Certain birds are protected under the Migratory Bird Treaty Act and the Bald and Golden Eagle
Protection Act .
Any person or organization who plans or conducts activities that may result in impacts to
migratory birds, eagles, and their habitats should follow appropriate regulations and consider
implementing appropriate conservation measures, as described below.
1.The Migratory Birds Treaty Act of 1918.
2.The Bald and Golden Eagle Protection Act of 1940.
3.50 C.F.R. Sec. 10.12 and 16 U.S.C. Sec. 668(a)
The birds listed below are birds of particular concern either because they occur on the USFWS
Birds of Conservation Concern (BCC) list or warrant special attention in your project location.
To learn more about the levels of concern for birds on your list and how this list is generated, see
the FAQ below. This is not a list of every bird you may find in this location, nor a guarantee that
every bird on this list will be found in your project area. To see exact locations of where birders
and the general public have sighted birds in and around your project area, visit the E-bird data
mapping tool (Tip: enter your location, desired date range and a species on your list). For
projects that occur off the Atlantic Coast, additional maps and models detailing the relative
occurrence and abundance of bird species on your list are available. Links to additional
information about Atlantic Coast birds, and other important information about your migratory
bird list, including how to properly interpret and use your migratory bird report, can be found
below.
For guidance on when to schedule activities or implement avoidance and minimization measures
to reduce impacts to migratory birds on your list, click on the PROBABILITY OF PRESENCE
SUMMARY at the top of your list to see when these birds are most likely to be present and
breeding in your project area.
NAME
BREEDING
SEASON
Bald Eagle Haliaeetus leucocephalus
This is not a Bird of Conservation Concern (BCC) in this area, but warrants attention
because of the Eagle Act or for potential susceptibilities in offshore areas from certain types
of development or activities.
https://ecos.fws.gov/ecp/species/1626
Breeds Sep 1 to
Jul 31
Blue-winged Warbler Vermivora pinus
This is a Bird of Conservation Concern (BCC) only in particular Bird Conservation Regions
(BCRs) in the continental USA
Breeds May 1
to Jun 30
1
2
07/17/2018 Event Code: 04EN1000-2018-E-01573   2

NAME
BREEDING
SEASON
Eastern Whip-poor-will Antrostomus vociferus
This is a Bird of Conservation Concern (BCC) throughout its range in the continental USA
and Alaska.
Breeds May 1
to Aug 20
Prairie Warbler Dendroica discolor
This is a Bird of Conservation Concern (BCC) throughout its range in the continental USA
and Alaska.
Breeds May 1
to Jul 31
Red-headed Woodpecker Melanerpes erythrocephalus
This is a Bird of Conservation Concern (BCC) throughout its range in the continental USA
and Alaska.
Breeds May 10
to Sep 10
Rusty Blackbird Euphagus carolinus
This is a Bird of Conservation Concern (BCC) throughout its range in the continental USA
and Alaska.
Breeds
elsewhere
Wood Thrush Hylocichla mustelina
This is a Bird of Conservation Concern (BCC) throughout its range in the continental USA
and Alaska.
Breeds May 10
to Aug 31
Probability Of Presence Summary
The graphs below provide our best understanding of when birds of concern are most likely to be
present in your project area. This information can be used to tailor and schedule your project
activities to avoid or minimize impacts to birds. Please make sure you read and understand the
FAQ “Proper Interpretation and Use of Your Migratory Bird Report” before using or attempting
to interpret this report.
Probability of Presence ()
Each green bar represents the bird's relative probability of presence in the 10km grid cell(s) your
project overlaps during a particular week of the year. (A year is represented as 12 4-week
months.) A taller bar indicates a higher probability of species presence. The survey effort (see
below) can be used to establish a level of confidence in the presence score. One can have higher
confidence in the presence score if the corresponding survey effort is also high.
How is the probability of presence score calculated? The calculation is done in three steps:
1.The probability of presence for each week is calculated as the number of survey events in
the week where the species was detected divided by the total number of survey events for
that week. For example, if in week 12 there were 20 survey events and the Spotted Towhee
was found in 5 of them, the probability of presence of the Spotted Towhee in week 12 is
0.25.
2.To properly present the pattern of presence across the year, the relative probability of
presence is calculated. This is the probability of presence divided by the maximum
07/17/2018 Event Code: 04EN1000-2018-E-01573   3

probability of presence across all weeks. For example, imagine the probability of presence
in week 20 for the Spotted Towhee is 0.05, and that the probability of presence at week 12
(0.25) is the maximum of any week of the year. The relative probability of presence on
week 12 is 0.25/0.25 = 1; at week 20 it is 0.05/0.25 = 0.2.
3.The relative probability of presence calculated in the previous step undergoes a statistical
conversion so that all possible values fall between 0 and 10, inclusive. This is the
probability of presence score.
Breeding Season ()
Yellow bars denote a very liberal estimate of the time-frame inside which the bird breeds across
its entire range. If there are no yellow bars shown for a bird, it does not breed in your project
area.
Survey Effort ()
Vertical black lines superimposed on probability of presence bars indicate the number of surveys
performed for that species in the 10km grid cell(s) your project area overlaps. The number of
surveys is expressed as a range, for example, 33 to 64 surveys.
No Data ()
A week is marked as having no data if there were no survey events for that week.
Survey Timeframe
Surveys from only the last 10 years are used in order to ensure delivery of currently relevant
information. The exception to this is areas off the Atlantic coast, where bird returns are based on
all years of available data, since data in these areas is currently much more sparse.
SPECIES JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC
Bald Eagle
Non-BCC Vulnerable
Blue-winged
Warbler
BCC - BCR
Eastern Whip-poor-
will
BCC Rangewide (CON)
Prairie Warbler
BCC Rangewide (CON)
Red-headed
Woodpecker
BCC Rangewide (CON)
Rusty Blackbird
BCC Rangewide (CON)
Wood Thrush
BCC Rangewide (CON)
no data survey effort breeding season probability of presence
07/17/2018 Event Code: 04EN1000-2018-E-01573   4

Additional information can be found using the following links:
▪Birds of Conservation Concern http://www.fws.gov/birds/management/managed-species/
birds-of-conservation-concern.php
▪Measures for avoiding and minimizing impacts to birds http://www.fws.gov/birds/
management/project-assessment-tools-and-guidance/
conservation-measures.php
▪Nationwide conservation measures for birds http://www.fws.gov/migratorybirds/pdf/
management/nationwidestandardconservationmeasures.pdf
Migratory Birds FAQ
Tell me more about conservation measures I can implement to avoid or minimize impacts
to migratory birds.
Nationwide Conservation Measures describes measures that can help avoid and minimize
impacts to all birds at any location year round. Implementation of these measures is particularly
important when birds are most likely to occur in the project area. When birds may be breeding in
the area, identifying the locations of any active nests and avoiding their destruction is a very
helpful impact minimization measure. To see when birds are most likely to occur and be breeding
in your project area, view the Probability of Presence Summary. Additional measures and/or
permits may be advisable depending on the type of activity you are conducting and the type of
infrastructure or bird species present on your project site.
What does IPaC use to generate the migratory birds potentially occurring in my specified
location?
The Migratory Bird Resource List is comprised of USFWS Birds of Conservation Concern
(BCC) and other species that may warrant special attention in your project location.
The migratory bird list generated for your project is derived from data provided by the Avian
Knowledge Network (AKN). The AKN data is based on a growing collection of survey, banding,
and citizen science datasets and is queried and filtered to return a list of those birds reported as
occurring in the 10km grid cell(s) which your project intersects, and that have been identified as
warranting special attention because they are a BCC species in that area, an eagle (Eagle Act
requirements may apply), or a species that has a particular vulnerability to offshore activities or
development.
Again, the Migratory Bird Resource list includes only a subset of birds that may occur in your
project area. It is not representative of all birds that may occur in your project area. To get a list
of all birds potentially present in your project area, please visit the E-bird Explore Data Tool.
What does IPaC use to generate the probability of presence graphs for the migratory birds
potentially occurring in my specified location?
07/17/2018 Event Code: 04EN1000-2018-E-01573   5

The probability of presence graphs associated with your migratory bird list are based on data
provided by the Avian Knowledge Network (AKN). This data is derived from a growing
collection of survey, banding, and citizen science datasets .
Probability of presence data is continuously being updated as new and better information
becomes available. To learn more about how the probability of presence graphs are produced and
how to interpret them, go the Probability of Presence Summary and then click on the "Tell me
about these graphs" link.
How do I know if a bird is breeding, wintering, migrating or present year-round in my
project area?
To see what part of a particular bird's range your project area falls within (i.e. breeding,
wintering, migrating or year-round), you may refer to the following resources: The Cornell Lab
of Ornithology All About Birds Bird Guide, or (if you are unsuccessful in locating the bird of
interest there), the Cornell Lab of Ornithology Neotropical Birds guide. If a bird on your
migratory bird species list has a breeding season associated with it, if that bird does occur in your
project area, there may be nests present at some point within the timeframe specified. If "Breeds
elsewhere" is indicated, then the bird likely does not breed in your project area.
What are the levels of concern for migratory birds?
Migratory birds delivered through IPaC fall into the following distinct categories of concern:
1."BCC Rangewide" birds are Birds of Conservation Concern (BCC) that are of concern
throughout their range anywhere within the USA (including Hawaii, the Pacific Islands,
Puerto Rico, and the Virgin Islands);
2."BCC - BCR" birds are BCCs that are of concern only in particular Bird Conservation
Regions (BCRs) in the continental USA; and
3."Non-BCC - Vulnerable" birds are not BCC species in your project area, but appear on
your list either because of the Eagle Act requirements (for eagles) or (for non-eagles)
potential susceptibilities in offshore areas from certain types of development or activities
(e.g. offshore energy development or longline fishing).
Although it is important to try to avoid and minimize impacts to all birds, efforts should be made,
in particular, to avoid and minimize impacts to the birds on this list, especially eagles and BCC
species of rangewide concern. For more information on conservation measures you can
implement to help avoid and minimize migratory bird impacts and requirements for eagles,
please see the FAQs for these topics.
Details about birds that are potentially affected by offshore projects
For additional details about the relative occurrence and abundance of both individual bird species
and groups of bird species within your project area off the Atlantic Coast, please visit the
Northeast Ocean Data Portal. The Portal also offers data and information about other taxa besides
birds that may be helpful to you in your project review. Alternately, you may download the bird
model results files underlying the portal maps through the NOAA NCCOS Integrative Statistical
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Modeling and Predictive Mapping of Marine Bird Distributions and Abundance on the Atlantic
Outer Continental Shelf project webpage.
Bird tracking data can also provide additional details about occurrence and habitat use
throughout the year, including migration. Models relying on survey data may not include this
information. For additional information on marine bird tracking data, see the Diving Bird Study
and the nanotag studies or contact Caleb Spiegel or Pam Loring.
What if I have eagles on my list?
If your project has the potential to disturb or kill eagles, you may need to obtain a permit to avoid
violating the Eagle Act should such impacts occur.
Proper Interpretation and Use of Your Migratory Bird Report
The migratory bird list generated is not a list of all birds in your project area, only a subset of
birds of priority concern. To learn more about how your list is generated, and see options for
identifying what other birds may be in your project area, please see the FAQ “What does IPaC
use to generate the migratory birds potentially occurring in my specified location”. Please be
aware this report provides the “probability of presence” of birds within the 10 km grid cell(s) that
overlap your project; not your exact project footprint. On the graphs provided, please also look
carefully at the survey effort (indicated by the black vertical bar) and for the existence of the “no
data” indicator (a red horizontal bar). A high survey effort is the key component. If the survey
effort is high, then the probability of presence score can be viewed as more dependable. In
contrast, a low survey effort bar or no data bar means a lack of data and, therefore, a lack of
certainty about presence of the species. This list is not perfect; it is simply a starting point for
identifying what birds of concern have the potential to be in your project area, when they might
be there, and if they might be breeding (which means nests might be present). The list helps you
know what to look for to confirm presence, and helps guide you in knowing when to implement
conservation measures to avoid or minimize potential impacts from your project activities,
should presence be confirmed. To learn more about conservation measures, visit the FAQ “Tell
me about conservation measures I can implement to avoid or minimize impacts to migratory
birds” at the bottom of your migratory bird trust resources page.
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Wetlands
Impacts to NWI wetlands and other aquatic habitats may be subject to regulation under Section
404 of the Clean Water Act, or other State/Federal statutes.
For more information please contact the Regulatory Program of the local U.S. Army Corps of
Engineers District.
Please note that the NWI data being shown may be out of date. We are currently working to
update our NWI data set. We recommend you verify these results with a site visit to determine
the actual extent of wetlands on site.
FRESHWATER FORESTED/SHRUB WETLAND
▪PFO1A
FRESHWATER POND
▪PUBHh
RIVERINE
▪R2UBHx
▪R4SBC