20190289 Ver 1_20190926 Publix RFI II Package_20191007

Staff Review
Does this application have all the attachments needed to accept it into the review process?
r Yes r No
ID#* Version* 1
20190289
Is this project a public transportation project?* r Yes
r No
Reviewer List:* Sue Homewood:eads\slhomevtood
Select Reviewing Office:* Winston-Salem Regional Office - [phone]
Submittal Type:*
Application Attachments
Does this project require a request for payment to be sent?*
r
Yes
r
No

Project Submittal Form
Please note: fields marked with a red asterisk below are required. You will not be able to submit the form until all
mandatory questions are answered.
Project Type: r New Project
r Pre -Application Submittal
r More Information Response
r Other Agency Comments
r For the Record Only (Courtesy Copy)
r Stream or Buffer Appeal
New Project - Please check the new project type if you are trying to submit a new project that needs an official approval
decision.
Pre -Application Submittal - Please check the pre -application submittal if you just want feedback on your submittal and
do not have the expectation that your submittal will be considered a complete application requiring a formal decision.
More Information Response - Please check this type if you are responding to a request for information from staff and
you have and ID# and version for this response.
Other Agency Comments - Please check this if you are submitting comments on an existing project.
Is this supplemental information that needs to be sent to the Corps?*
r Yes r No
Project Contact Information
Name: Brian Breissinger
Who is subrritting the inforrration?
Email Address: [e-mail]
Project Information
Existing ID #: Existing Version:
20190289 1
20170001 (no dashes)
Project Name: Publix Distribuation Center
Is this a public transportation project?
r Yes
r No
Is the project located within a NC DCM Area of Environmental Concern (AEC)?
r Yes r No r Unknown
County (ies)
Guilford
Please upload all files that need to be submited.
Click the upload button or drag and drop files here to attach docurrent
20190926 Publix RFI II Package.pdf 42.2MB
Only pdf or IOIY files are accepted.
Describe the attachments:

Please find attached response to the request for additional information for the Publix Distribution Facility in
Guilford County, NC. DWR #20190289 and USACE #SAW -2018-00240.
V By checking the box and signing box below, I certify that:
• I have given true, accurate, and complete information on this form;
• I agree that submission of this form is a "transaction" subject to Chapter 66, Article 40 of the NC General Statutes (the
"Uniform Electronic Transactions Act")
• I agree to conduct this transaction by electronic means pursuant to Chapter 66, Article 40 of the NC General Statutes
(the "Uniform Electronic Transactions Act');
• I understand that an electronic signature has the same legal effect and can be enforced in the same way as a written
signature; AND
• I intend to electronically sign and submit the online form."
Signature:
Submittal Date: Is filled inautorretically.

•0000
0
TIMMONS GROUP
YOUR VISION ACHIEVED THROUGH OURS.
Mr. David E. Bailey
Regulatory Project Manager
USACE Raleigh Regulatory Field Office
3331 Heritage Trade Drive, Suite 105
Wake Forest, North Carolina 27587
Ms. Sue Homewood
Division of Water Resources
North Carolina Department of Environment
and Natural Resources
450 W. Hanes Mill Rd, Suite 300
Winston Salem, North Carolina 27105
1001 Boulders Parkway P 804.200.6500
Suite 300 F 804.560.1016
Richmond, VA 23225 www.timmons.com
October 4, 2019
Re: Request for Additional Information - Publix Distribution Center - (DWR: 20190289 &
USACE: SAW -2018-00240)
Mr. Bailey & Ms. Homewood,
Please find responses to the items requested by the North Carolina Division of Water
Resources (DWR) in an Additional Information Request Letter dated September 19, 2019 and
by the U.S. Army Corps of Engineers (USACE) in a letter dated September 7, 2019 in
association with a Request for Additional Information for the Individual Permit issuance for the
Publix Distribution Center project located in Guilford County, North Carolina.
Comments below from the DWR (in black) with responses
1) As the Division has the same questions and concerns raised by the US Army Corps of
Engineers in their letter to you dated September 7, 2019, please provide the Division with a
copy of your response to items 3, 5 and 7 of their request. [1 SA NCAC 02H .0506(b)(4)]
Please see below for a response to Items 3, 5, and 7.
2) Please provide additional information regarding the indirect and cumulative impact analysis
that you have provided for the project. Specifically, your analysis indicates that the project
will likely stimulate growth. The sequential following question posed by the Division's policy
(http://portal.ncdenr.org/web/wg/swp/ws/401/policies) is "are the existing uses of the water
likely to be impacted by the growth [emphasis added]?" Your analysis provides information
regarding impacts to be expected from the Project, however the Division's policy is
specifically requesting an analysis of expected downstream water quality impacts as a result
of the growth that the project is likely to stimulate. [1 SA NCAC 02H .0506(b)(4)]
Thank you for clarification to the Divisions request. The Project is expected to provide a
significant number of jobs to the region. Specifically, it is anticipated that the approximately
1,000 -person workforce will be compiled from not only Guilford County, but also Alamance
and Orange Counties. As mentioned in the Indirect and Cumulative Impact Analysis dated
August 16, 2019, the projected workforce will come from a region characterized by low
CIVIL ENGINEERING I ENVIRONMENTAL I SURVEYING I GIS I LANDSCAPE ARCHITECTURE I CONSTRUCTION SERVICES

income and a significant unemployment rate. Furthermore, available jobs do not provide a
comparable wage or benefits as those related to the proposed Project. We anticipate that
this Project will not lead to a local population increase but will provide economic opportunity
to the currently unemployed residents. Thus, we do not anticipate any indirect impacts to the
Waters as related to population growth associated with the Project. The projected growth is
related to economic opportunity and livelihood, and an increase in localized population
density is not anticipated. Any incidental population growth attributed to additional small
business, gas stations, etc. will be addressed in the respective projects' erosion and
sediment control and stormwater management plan review. Existing uses of Waters would
be consistent with pre -development conditions.
Comments below from the USA CE (in black) with responses (in red):
1) Thank you for the additional information provided in response to items A.i, A.ii.a-h, A.iii, A.iv,
B.i, C.ii, 1, and 2.b -d in our previous letter. At this point in our evaluation we believe that you
provided sufficient information to resolve those questions. However, please note that we
may request additional information pertaining to those items during the preparation of our
Environmental Assessment if needed;
Acknowledged
2) Your letter made reference to one or more off-site alternatives not being the least
environmentally damaging based on remotely sensed assumption of aquatic resources.
Specifically, the Guilford College Road off-site alternative was developed and described in
your letter. In addition to providing the aerial photograph of this new alternative (attachment
6) showing streams and wetlands from the National Hydrography Dataset and National
Wetlands Inventory, respectively, please also quantify these assumed aquatic resources to
allow for a comparison with the preferred alternative. Also, please provide the same figures
and quantified information for the Reedy Fork and Youngs Mill alternatives. (see item A.ii.i in
our previous letter);
Please see Attachment 1: Offsite Alternative Analysis for revised maps with quantified
assumed aquatic resource impacts.
3) Revisions needed for plan sheets:
a) Revise the project plan sheets such that waters of the US are labeled using the same
labels as those on the Approved Jurisdictional Determination signed survey (see item 2a
in our previous letter);
Please see Attachment 2: Project Plan Sheets for revised plan sheets
b) On the "Preliminary Jurisdictional Waters of the US Impacts Map- Table" (Sheet 13 of
13), add a column for each impact that identifies the waters of the US proposed for
impact using the same labels as those on the Approved Jurisdictional Determination
signed survey. Also, impacts to each separate water should be quantified/itemized
separately (e.g., Impact SI includes impacts to both Stream K and Stream 0; Impact W18
includes impacts to W10A, W10B, WI1, WI2, W13; etc.);
Please see Attachment 3: Preliminary Jurisdictional Waters of the US Impacts Map for
revised impacts map and tables. Please note, impacts to separate waters have been
itemized separately.
4) Thank you for including proposed compensatory mitigation ratios in your "Preliminary
CIVIL ENGINEERING I ENVIRONMENTAL I SURVEYING I GIS I LANDSCAPE ARCHITECTURE I CONSTRUCTION SERVICES

Jurisdictional Waters of the US Impacts Map- Table." However, given the proposed method
of providing compensatory mitigation (NCDMS) and as previously discussed, any reduction
below a 2:1 mitigation to impact ratio must be justified based on resource quality, rather than
simply stream flow regime. As such, please provide NCSAM/NCW AM forms for those
impacts/reaches where an impact mitigation ratio of less than 2:1 is proposed (see item C.i
in our previous letter);
Please see Attachment 4: NC SAM Evaluation Package for documentation of the NC SAM
evaluation. Included in that package is proposed mitigation ratios for the impacts to
jurisdictional features.
5) Thank you for your Indirect and Cumulative Impact Analysis. After review of your project
plans we continue to be concerned that there is a reasonable expectation that the proposed
fill activities would result in the dewatering of down -gradient stream channels and wetlands
(i.e., indirect impacts associated with proposed fill activities). Specifically:
a) Impact W2: remaining section of Wetland W29 would be too small to retain function and
would lose its watershed;
Acknowledged. Remaining section of Wetland W29 has been added as a proposed
impact.
b) Impact W19: remaining section of Wetland W6 and possibly Stream H would lose its
watershed;
An additional 3,461 sf of Wetland W6 has been accounted for as a secondary impact.
The remaining portion of Wetland W6 and Stream H will remain hydrated from post
construction contours that would create a laminar flow downslope into the Wetland W6
and Stream H. Additionally, roadside drainage is expected to continue hydrating these
Features, and total loss of hydrology is no anticipated.
c) Impact S1: Stream K would lose its watershed and it is not clear that the adjacent
stormwater outfall would provide sufficient hydrology to the remaining length;
The physical location of the outfall has been moved to further hydrate the remaining
stream. The Applicant is proposing the connection of the water quality orifice to the tail
end of the remainder of stream K. This will include an 8" diameter orifice that is set at
the normal pool elevation of the pond. This orifice will discharge stormwater run-off
collected in the pond down to normal pool elevation. Thus, a impactful amount of water
will be draining into the stream during and for a relatively long duration following rain
events. This stormwater pond drains 43.3 -acres of the developed site, so a
considerable volume of water will drain through the orifice, and into the stream following
rainfall events.
d) Impact S3: Stream S 1 would lose its watershed and it is not clear that the adjacent
stormwater outfall would provide sufficient hydrology to the remaining length;
An additional 31 If of Stream S1 has been proposed as a secondary impact. It is not
feasible to route the water quality orifice or the water quantity control riser to the far
upstream reach of the remainder of Stream S1. However, this area is in or very near
FEMA Floodplain and Floodway and the remaining area will be hydrated via sheet flow
from the existing topography.
CIVIL ENGINEERING I ENVIRONMENTAL I SURVEYING I GIS I LANDSCAPE ARCHITECTURE I CONSTRUCTION SERVICES

e) Impact W10: Stream I and Wetland W17 would lose their watershed and it is not clear
that the adjacent storm water outfall would provide sufficient hydrology to their remaining
length/area;
The remaining 85 sf of Wetland W17 has been proposed as a secondary impact. While
we agree that a portion of the contributing drainage basin to Stream I is cut off by the
proposed improvements, there still is a significant portion of the contributing basin
between the project and the stream and south of the stream which will remain. As such,
there will still be significant base flow and run-off that will hydrate the stream. Due to the
location of the stream in relation to the project stormwater management system, we
cannot route project stormwater into the upper reaches of this stream. Additionally, the
intermittent nature of the stream will be maintained as it is still located within its natural
topographic draw, allowing water to naturally hydrate the feature.
f) Impact S7: Stream F and Wetlands 14A and B would lose their watershed and it is not
clear that the adjacent stormwater outfall would provide sufficient hydrology to their
remaining length/area;
The outfall location has been physically moved to improve hydrology to the remaining
stream channel. We are proposing the connection of the water quality orifice to the tail
end of the remainder of stream F. This will include an 12" diameter orifice that is set at
the normal pool elevation of the pond. This orifice will discharge stormwater run-off
collected in the pond down to normal pool elevation. Thus, a impactful amount of water
will be draining into the stream during and for a relatively long duration following rain
events. This stormwater pond drains 94.2 -acres of the developed site, so a
considerable volume of water will drain through the orifice, and into the stream following
rainfall events.
6) As you are aware, consultation with the State Historic Preservation Office is ongoing
pursuant to Section 106 ofthe National Historic Preservation Act. Please note that we cannot
authorize impacts to waters of the US prior to completion of the Section 106 consultation
process.
Acknowledged.
7) Please see the attached comments from the North Carolina Wildlife Resources commission
(NCWRC), dated June 10, 2019;
The Applicant has retained Three Oaks Engineering, Inc. to conduct a freshwater mussel
and crayfish surveys on the Site. Field work was conducted on September 19, 2019, and a
formal report will be submitted to WRC. The Corps and DWR will be copied on the
correspondence to WRC. The survey identified no evidence of habitat to support freshwater
mussels. Crayfish were observed and compared to museum samples to confirm they are not
the Greensboro Burrowing Crayfish.
8) Please note that responses to the questions above may prompt additional information
requests to allow full evaluation of the proposed project.
Acknowledged.
CIVIL ENGINEERING I ENVIRONMENTAL I SURVEYING I GIS I LANDSCAPE ARCHITECTURE I CONSTRUCTION SERVICES

Please feel free to contact Brian Breissinger at (804)-200-6439, or by email at
brian.breissinaer(c�timmons.com if you have any questions.
Sincerely,
Timmons Group
Brian Breissinger
Environmental Services Manager
Attachments:
1. Offsite Alternatives Analysis
2. Project Plans Sheets
3. Preliminary Jurisdictional Waters of the US Impacts Map
4. NC SAM Evaluation Package
Cc (by e-mail):
Jay Matey, PE, Timmons Group
Brian Crutchfield, PE, Timmons Group
Robin Perez, Timmons Group
John Fisher, Publix
CIVIL ENGINEERING I ENVIRONMENTAL I SURVEYING I GIS I LANDSCAPE ARCHITECTURE I CONSTRUCTION SERVICES

Attachment
Offsite Alternatives Analysis

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Limits of Disturbance - 231.3 Acres
© Stream Impact
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Zone 1 Buffer Impact - Temporary
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Impacts Table
Wetland (sq. ft) Stream Buffers (sq. ft) Stream (If)
Impact Conversion Impact Impact Resource Mitigation Stream Wetland Buffer Confirmed
Impact ID Permanent T..__ Mitigation I Mitigation Mitigation Delineation
W11
142
W2
2:1
764
W 3-A
87
W 3-B
5,035
W3 -C
2:1
1,081
W4
1,468
W 5-A
64,480
W 5-B
2:1
2,483
W6
2,281
W7
9,160
W8
2:1
255
W9
976
W10
285
W11
2:1
519
W 12-A
810
W 12-B
472
W13
2:1
5,896
W14
-
7,167
W15
132
W16
NR
67
W17
-
87
W 18-A
422
W 18-B
W 18-C
W 18-D
W 18-E
1:1
376
191
822
1,543
4,935
W19
S1 -A
-
S1 -B
S1 -C
S2
S3
2:1
S4
4,562
S5
S6
S7 -A
S7 -B
S7 -C
S8
W35
S9
B2 -Z1
B2 -Z2
POW
NR
B3 -Z1
-
-
Pond 2
B3 -Z2
PFO
2:1
-
B4 -Z2
B5 -Z2
B6 -Z1
B6 -Z2
-
W36
B7 -Z1
PFO
2:1
-
1,952
B7 -Z2
0 sq ft
73,640 s ft
38,296 sq ft
0 sq ft
Total
0.0 ac
1.7 ac
0.9 ac
0.0 ac
NR = Not Required for Mitigation
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10,070
W30
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W31
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W34
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W38
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W35
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PFO
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W37
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570
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W4
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1,620
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W313
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14,334
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W1
PFO
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264
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W8
PFO
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134
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W9
PFO
2:1
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174
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W23
PFO
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844
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W 10A
PFO
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752
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382
Will
PFO
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1,644
W12
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3,086
W13
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9,870
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W6
290
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580
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K
687
R4
1:1
687
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28
R4
1:1
28
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O
318
R4
1:1
318
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L
204
R3
2:1
408
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S1
283
R4
1:1
283
-
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S1
57
R4
1:1
57
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S11
373
R4
1:1
373
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1,480
R3
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2,960
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F
707
R4
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707
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94
Zone 2
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53,609
Zone 1
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160,827
39,241
Zone 2
1.5:1
-
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58,862
1,880
Zone 2
NR
-
-
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1,975
Zone 2
NR
-
-
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1,707
Zone 1
NR
-
-
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611
Zone 2
NR
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1,561
Zone 1
NR
-
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1,023
Zone 2
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96,804 sq ft52 If
4,482 If
-
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Attachment 3:
Preliminary Jurisdictional Waters of the US Impacts Map

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-----
Stream Buffers
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DATE
12/18/2018
PROJECT NUMBER
42407
PROJECT NAME
PUBLIX
DESIGNED BY / DRAWN BY
L. MAJOR
1. Waters of the U.S. within the
project study limits have been
located using submeter, Bluetooth
GPS antennas by others.
2.Waters of the U.S. have been
confirmed by the U.S. Army Corps
of Engineers.
3. Project limits are approximate.
4. Topography based on USGS
Li DAR.
5. Cowardin Stream
Classifications are based on
confirmed Perennial Flow
Determination.
These plans and associated documents are the
exclusive property of TIMMONS GROUP and
may not be reproduced in whole or in part and
shall not be used for any purpose whatsoever,
inclusive, but not limited to construction, bidding,
and/or construction staking without the express
written consent ofTIMMONS GROUP.
DRAWING DESCRIPTION
PRELIMINARY
JURISDICTIONAL
WATERS OF THE
U.S. IMPACTS MAP
SCALE (FEET)
O 40
0
PLANS PRINTEDAS ARE HALF SCALE
SCALE I SHEET NUMBER
1-1:1 " = 4001 1 OF 12
etland Impacts\42407-WTIM.mxd
REVISIONS
# MM/DD/YY
DESCRIPTION
1 08/14/19
Impacts updated per revised layout.
2 09/17/19
Impact ID's updated.
3 09/25/19
Impacts updated per revised layout.
DRAWING DESCRIPTION
PRELIMINARY
JURISDICTIONAL
WATERS OF THE
U.S. IMPACTS MAP
SCALE (FEET)
O 40
0
PLANS PRINTEDAS ARE HALF SCALE
SCALE I SHEET NUMBER
1-1:1 " = 4001 1 OF 12
etland Impacts\42407-WTIM.mxd

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DESCRIPTION
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Impacts updated per revised layout.
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Impact ID's updated.
3 09/25/19
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exclusive property of TIMMONS GROUP and
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and/or construction staking without the express
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DATE
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PROJECT NUMBER
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PROJECT NAME
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# MM/DD/YY
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# MM/DD/YY
DESCRIPTION
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DATE
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PROJECT NUMBER
42407
PROJECT NAME
PUBLIX
DESIGNED BY/ DRAWN BY
L. MAJOR
1. Waters of the U.S. within the
project study limits have been
located using submeter, Bluetooth
GPS antennas by others.
2.Waters of the U.S. have been
confirmed by the U.S. Army Corps
of Engineers.
3. Project limits are approximate.
4. Topography based on USGS
Li DAR.
5. Cowardin Stream
Classifications are based on
confirmed Perennial Flow
Determination.
f" I
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I , These plans and associated documents are the
exclusive property of TIMMONS GROUP and
r may not be reproduced in whole or in part and
1 1 shall not be used for any purpose whatsoever,
1 inclusive, but not limited to construction, bidding,
and/or construction staking without the express
written consent ofTIMMONS GROUP.
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# MM/DD/YY
DESCRIPTION
1 08/14/19
Impacts updated per revised layout.
2 09/17/19
Impact ID's updated.
3 09/25/19
Impacts updated per revised layout.
DRAWING DESCRIPTION
PRELIMINARY
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a L r� lip J~ ■ 'Pp. ! , , i i t , ` ` \ - 1 , - \ L , L 1 , J 1 , 1 1 t , 1 L , t \ , 1 �.
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PROJECT NAME &LOCATION
Legend ri '`. `\, `-, `�, - .` `' ', '' ', ,,J;;,- ____\ 1 ,+ \'_.= _.��\ ,M,,� �
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354.2 Acres
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o Limits of Disturbance - 231.2 Acres
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_
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Zone 2 Buffer Impact - Permanent
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r
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1 08/14/19
` _ - _ -
2 09/17/19
Impact ID's updated.
3 09/25/19
Impacts updated per revised layout.
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Legend ri '`. `\, `-, `�, - .` `' ', '' ', ,,J;;,- ____\ 1 ,+ \'_.= _.��\ ,M,,� �
�`♦ \. W
!r—
354.2 Acres
Project Limits -
W
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o Limits of Disturbance - 231.2 Acres
, I'
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50
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_
Zone 1 Buffer Impact - Temporary j `:__- --_ ;', _ `\ `.
Zone 2 Buffer Impact - Permanent
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r
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1 08/14/19
` _ - _ -
2 09/17/19
Impact ID's updated.
3 09/25/19
Impacts updated per revised layout.
-
Perennial Stream (R3)--
1
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`
Permanent Stream Impact
1
\
DATE
12/18/2018
PROJECT NUMBER
42407
PROJECT NAME
PUBLIX
DESIGNED BY/ DRAWN BY
L. MAJOR
'
-
hin
Temporary Stream Impact - - �' ` - - - r 1.Waters
tudyli U.S.vebethe
1 fJ , , 4 y �r 4 1 11 f \ , •,•
-_ , + r ti, 'y\ - _ - _ �\ project study limits have been
located using submeter, Bluetooth
-
f -Y` GPS antennas by others.
Secondary Stream Impacts _ - -
I ' � 1 ' '• ,' I � ' r I1 1 ,I � r,\ \ \ ��; L, � � = ' 1 _ 2. Waters of the U.S. have been
`r \`, confirmed by the U.S. Army Corps
l` - r - of Engineers.
%
Stream Top of Bank -' 1 ' - 3. Project limits are approximate.
f I ,!-'r � r' r r'r � ' 4. Topography based on USGS
r /' -r- , 1 -• ~`, 1 / r r _ , r , . , f + , , , , �` , i' ' y / —� \ -- LiDAR.
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r , .`, , \ q� - 5. Cowardin Stream
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1 I
Elk Palustrine Emergent (PEM) Wetland
Determination.
-
- r
Palustrine Open Water (POW) - - - - -
I r I 1 \ \ , I 1 1 • I 1 [ f I ' - I r / r r , 1 ,' ,/ 1 I I I1 , I ' \ 1 1 r f Il t r 1 1
,' r ', r _ r 'y , !' ! r + ! z' r , \ r_ 1 - _ These plans and associated documents are the
Wetland Impacts ' ' \+ - - _ _ _ r r q ' r , I ' ' - _ exclusive property of TIMMONS GROUP and
I I _ , `, I y I f f _ may not be reproduced in whole or in part and
' shall not be used for any purpose whatsoever,
inclusive, but not limited to construction, bidding,
_ _ and/or construction staking the.
expressSecondary Wetland Impacts written consent ofTMMONSGROUP
\ \
NC DOT TIP Project: U-2581 BA - 15.1 Acres
1
-
4`
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11
SCALE (FEET)
_- ----- -_ 0 50 100
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' _ ` L • , 1 , , `, ' '_ SCALE SHEET NUMBER
\
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-
Y:\805\42407-Publix Distribution Center\GIS\Wetland Impacts\42407-WTIM.nnxd
REVISIONS
# MM/DD/YY
DESCRIPTION
1 08/14/19
Impacts updated per revised layout.
2 09/17/19
Impact ID's updated.
3 09/25/19
Impacts updated per revised layout.
-
1
, 1
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l
[ /
11
SCALE (FEET)
_- ----- -_ 0 50 100
PLANS PRINTED AS 11X17 ARE HALF SCALE
' _ ` L • , 1 , , `, ' '_ SCALE SHEET NUMBER
\
I-1:1' =50' 8OF 12
-
Y:\805\42407-Publix Distribution Center\GIS\Wetland Impacts\42407-WTIM.nnxd
REVISIONS
# MM/DD/YY
DESCRIPTION
1 08/14/19
Impacts updated per revised layout.
2 09/17/19
Impact ID's updated.
3 09/25/19
Impacts updated per revised layout.
[ /
11
SCALE (FEET)
_- ----- -_ 0 50 100
PLANS PRINTED AS 11X17 ARE HALF SCALE
' _ ` L • , 1 , , `, ' '_ SCALE SHEET NUMBER
\
I-1:1' =50' 8OF 12
-
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Secondary Stream Impacts - - `f' 1' 1\ \ - _ _ - -, -_ _ _ --_ - - - -; - _ _ ' - l // `+1 + I+
+ I + r I'
Stream Top of Bank --- - -- -'--_ - = l - - ==--- `---- - , + ,
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DATE
12/18/2018
PROJECT NUMBER
42407
PROJECT NAME
PUBLIX
DESIGNED BY / DRAWN BY
L. MAJOR
1. Waters of the U.S. within the
project study limits have been
located using submeter, Bluetooth
GPS antennas by others.
2.Waters of the U.S. have been
confirmed by the U.S. Army Corps
of Engineers.
3. Project limits are approximate.
4. Topography based on USGS
Li DAR.
5. Cowardin Stream
Classifications are based on
confirmed Perennial Flow
Determination.
These plans and associated documents are the
exclusive property of TIMMONS GROUP and
may not be reproduced in whole or in part and
shall not be used for any purpose whatsoever,
inclusive, but not limited to construction, bidding,
and/or construction staking without the express
written consent ofTIMMONS GROUP.
DRAWING DESCRIPTION
PRELIMINARY
JURISDICTIONAL
WATERS OF THE
U.S. IMPACTS MAP
- \ \ _ 1 1 ♦ � , ,r 9 Ir I , j / � � I I + I I I I V , � ,
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f - 'I I Y f L , , yf f +f „ 1 , I . I L \ • , , 0 50 100
' ' \ ♦ , + . PLANS PRINTED AS 11X17 ARE HALF SCALE
SCALE SHEET NUMBER
Il H:1"=50' 9OF12
'1 HHHf ` 4 , f i! '
Y:\805\42407-Publix Distribution Center\GIS\Wetland Impacts\42407-WTIM.nnxd
REVISIONS
# MM/DD/YY
DESCRIPTION
1 08/14/19
Impacts updated per revised layout.
2 09/17/19
Impact ID's updated.
3 09/25/19
Impacts updated per revised layout.
DRAWING DESCRIPTION
PRELIMINARY
JURISDICTIONAL
WATERS OF THE
U.S. IMPACTS MAP
- \ \ _ 1 1 ♦ � , ,r 9 Ir I , j / � � I I + I I I I V , � ,
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f - 'I I Y f L , , yf f +f „ 1 , I . I L \ • , , 0 50 100
' ' \ ♦ , + . PLANS PRINTED AS 11X17 ARE HALF SCALE
SCALE SHEET NUMBER
Il H:1"=50' 9OF12
'1 HHHf ` 4 , f i! '
Y:\805\42407-Publix Distribution Center\GIS\Wetland Impacts\42407-WTIM.nnxd

o
lan ❑r Qa
21
1
Project Limits - 354.2 Acres
DESCRIPTION
4
45
Limits of Disturbance - 231.2 Acres
o aDl
N.
♦'
■
7
'11 1 ;
` �.y
Legend
REVISIONS
Project Limits - 354.2 Acres
DESCRIPTION
1 08/14/19
LOD---1
o
Limits of Disturbance - 231.2 Acres
o aDl
3 09/25/19
©
Stream Impact
©
Wetland Impact
-----
Stream Buffers
\
f r
Zone 1 Buffer Impact - Permanent
q)
Zone 1 Buffer Impact - Temporary
/ I I 1 I
Zone 2 Buffer Impact - Permanent
Zone 2 Buffer Impact - Temporary
, f
, _
Perennial Stream (R3)
♦ I I
'
, '
!
Intermittent Stream (R4)
Jr 'f ,r
Permanent Stream Impact
t
Temporary Stream Impact
_
Secondary Stream Impacts
_
'♦ ,1 ' '
Stream Top of Bank
�
Palustrine Forested (PFO) Wetland
ElkL-
Palustrine Emergent (PEM) Wetland
,
Palustrine Open Water (POW)
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REVISIONS
# MM/DD/YY
DESCRIPTION
1 08/14/19
Impacts updated per revised layout.
2 09/17/19
Impact ID's updated.
3 09/25/19
Impacts updated per revised layout.
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# MM/DD/YY
DESCRIPTION
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2 09/17/19
Impact ID's updated.
3 09/25/19
Impacts updated per revised layout.
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DATE
12/18/2018
PROJECT NUMBER
42407
PROJECT NAME
PUBLIX
DESIGNED BY / DRAWN BY
L. MAJOR
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1. Waters of the U.S. within the
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located using submeter, Bluetooth
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3. Project limits are approximate.
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REVISIONS
# MM/DD/YY
DESCRIPTION
1 08/14/19
Impacts updated per revised layout.
2 09/17/19
Impact ID's updated.
3 09/25/19
Impacts updated per revised layout.
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DATE
12/18/2018
PROJECT NUMBER
42407
PROJECT NAME
PUBLIX
DESIGNED BY/ DRAWN BY
}lr ` L. MAJOR
, , 'I ! , !- ❑ ' �/'� !I I rf`\ ;i`I 1111 ,Y_ + I , I I I ■ ' `\, , , 4 _�! -
I
1. Waters of the U.S. within the
'
Temporary Stream Impact !�5_1 I r1 j_II+ ,
l Project study limits have been
_-------` _ __ Bluetooth
located using submeter, BI
� ';, ', � + r' GPS antennas by others
Secondary Stream Impacts _ -� rr - �`-- _ _ -- I r -- _ --- _ \ I`I
- r aD_ J 9 \ J - I !- 2.Waters of the U.S. have been
` =� I +� - confirmed by the U.S. Army Corps
I; :_----------- - i
'! f I r � I 1 J rf/�- ` +++ 11f' ' ' , ' + ' � - - - ` - - - ' \ li r � f 3. Project limits are approximate.
of Engineers.
Stream Top of Bank - ' --- ' '
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Perennial Flow
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-
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REVISIONS
# MM/DDNY
DESCRIPTION
1 08/14/19
Impacts updated per revised layout.
2 09/17/19
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3 09/25/19
Impacts updated per revised layout.
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REVISIONS
# MM/DDNY
DESCRIPTION
1 08/14/19
Impacts updated per revised layout.
2 09/17/19
Impact ID's updated.
3 09/25/19
Impacts updated per revised layout.
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Impacts Table
Impact ID
Wetland (sq.
ft)
Stream Buffers (sq. ft)
Stream (If)
Resource
Type
Mitigation
Ratio
Stream
Mitigation
Required
Wetland
Mitigation
Required
Buffer
Mitigation
Required
Confirmed
Delineation
Resource ID
Impact
Conversion
Impact
Impact
Temporary
Permanent
(Open
Water
Permanent
Temporary
Permanent
Temporary
Permanent
Temporary
Permanent
W1
0
M
142
m
OON
r
•
OLL�
11.DLo
2
PFO
2:1
-
284
-
W33
W2
�O
(Dz
fON�
vi
743
(�tD
r/
W
Y > 0 o
W
PFO
2:1
-
11486
-
W29
W2.2*
Q
�
nE
21
�
Zm
�
PFO
2:1
-
42
-
W29
W3 -A
87
PFO
2:1
-
174
-
W29
W3 -B
51035
PFO
2:1
-
101070
-
W30
W3 -C
11081
PFO
2:1
-
21162
-
W31
W4
11468
PFO
2:1
-
21936
-
W34
W5 -A
641480
POW
NR
-
-
-
Pond 1
W5 -B
21483
PEM
2:1
-
41966
-
W38
W6
21281
PFO
2:1
-
41562
-
W35
W7
91160
POW
NR
-
-
-
Pond 2
W8
255
PFO
2:1
-
510
-
W36
W9
976
PFO
2:1
-
11952
-
W37
W10
285
PFO
2:1
-
570
-
W17
W10.2*
85
PFO
2:1
-
170
-
W17
Wil
519
PFO
2:1
-
11038
-
W4
W12 -A-
810
PFO
2:1
-
11620
-
W3A
W 12-B
472
PFO
2:1
-
944
-
W3B
W13
51896
PFO
2:1
-
111792
-
W2
W14
71167
PFO
2:1
-
141334
-
W1
W15
132
PFO
2:1
-
264
-
W8
W16
67
PFO
2:1
-
134
-
W9
W17
87
PFO
2:1
-
174
-
W23
W 18-A
422
PFO
2:1
-
844
-
W 10A
W 18- B
376
PFO
2:1
-
752
-
W 10 B
W 18-C
191
PFO
2:1
-
382
-
Wil
W 18- D
822
PFO
2:1
-
11644
-
W12
W 18- E
1, 543
PFO
2:1
-
3, 086
-
W13
W19
411935
PFO
2:1
-
91870
-
W6
W19.2*
3,461
PFO
2:1
-
61922
-
W6
S 1-A
290
R3
2:1
580
-
-
K
S 1-B
687
R4
2:1
1, 374
-
-
K
S 1-C
28
R4
2:1
56
-
-
O
S2
318
R4
1.5:1
477
-
-
L
S3
204
R3
1:1
204
-
-
S1
S3.2*
31
R3
1.5:1
47
-
-
S1
S4
283
R4
1.5:1
425
-
-
S1
S5
57
R4
1:1
57
-
-
S1
S6
373
R4
2:1
746
-
-
H
S7 -A
17479
R3
2:1
2,958
-
-
F
S7 -B
707
R4
1.5:1
11061
-
-
F
S7 -C
55
R4
1.5:1
83
-
-
G
S8
10
R3
NR
-
-
-
J
S9
10
R3
NR
-
-
-
A
B3 -Z1
54, 295
Zone 1
3:1
-
-
162, 885
-
B3 -Z2
401628
Zone 2
1.5:1
-
-
601942
-
B4 -Z2
17880
Zone 2
NR
-
-
-
-
B6 -Z1
675
Zone 1
NR
-
-
-
-
B6 -Z2
245
Zone 2
NR
-
-
-
-
B7 -Z1
607
Zone 1
NR
-
-
-
-
B7 -Z2
405
Zone 2
NR
-
-
-
-
Total
0 sq ft
73, 640 sq ft
41, 842 sq ft
0 sq ft
0 sq ft
1, 932 sq ft
96, 803 sq ft
20 If
4, 512 If
-
-
8, 066 If
1.92 ac
223 827 sq ft
,
-
0.0 ac
1.7 ac
1.0 ac
0.0 ac
0.0 ac
0.04 ac
2.2 ac
5.14 ac
NR = Not Required for Mitigation
*Secondary impact
u
nter\GIS\Wetla
mpacl
PROJECT NAME 8. LOCATION
IL
V;
DESCRIPTION
1 08/14/19
LU
2 09/17/19
Impact ID's updated.
F -
Impacts updated per revised layout.
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PROJECT NAME 8. LOCATION
REVISIONS
W
DESCRIPTION
1 08/14/19
LU
2 09/17/19
Impact ID's updated.
F -
Impacts updated per revised layout.
z
LU
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a
DATE
12/18/2018
PROJECT NUMBER
42407
PROJECT NAME
PUBLIX
DESIGNED BY / DRAWN BY
L. MAJOR
1. Waters of the U.S. within the
project study limits have been
located using submeter, Bluetooth
GPS antennas by others.
2.Waters of the U.S. have been
confirmed by the U.S. Army Corps
of Engineers.
3. Project limits are approximate.
4. Topography based on USGS
Li DAR.
5. Cowardin Stream
Classifications are based on
confirmed Perennial Flow
Determination.
These plans and associated documents are the
exclusive property of TIMMONS GROUP and
may not be reproduced in whole or in part and
shall not be used for any purpose whatsoever,
inclusive, but not limited to construction, bidding,
and/or construction staking without the express
written consent ofTIMMONS GROUP.
DRAWING DESCRIPTION
PRELIMINARY
JURISDICTIONAL
WATERS OF THE
U.S. IMPACTS MAP
- TABLE
PLANS PRINTED AS 11X17 ARE HALF SCALE
SCALE SHEET NUMBER
H:1 " = 50' 12 OF 12
s\42407-WTIM - Table Sheet.mxd
REVISIONS
# MM/DD/YY
DESCRIPTION
1 08/14/19
Impacts updated per revised layout.
2 09/17/19
Impact ID's updated.
3 09/25/19
Impacts updated per revised layout.
DRAWING DESCRIPTION
PRELIMINARY
JURISDICTIONAL
WATERS OF THE
U.S. IMPACTS MAP
- TABLE
PLANS PRINTED AS 11X17 ARE HALF SCALE
SCALE SHEET NUMBER
H:1 " = 50' 12 OF 12
s\42407-WTIM - Table Sheet.mxd

Attachment 4:
NC SAM Evaluation Package
CIVIL ENGINEERING I ENVIRONMENTAL I SURVEYING I GIS I LANDSCAPE ARCHITECTURE I CONSTRUCTION SERVICES

•0000
0
TIMMONS GROUP
YOUR VISION ACHIEVED THROUGH OURS.
Mr. David E. Bailey
Regulatory Project Manager
USACE Raleigh Regulatory Field Office
3331 Heritage Trade Drive, Suite 105
Wake Forest, North Carolina 27587
Ms. Sue Homewood
Division of Water Resources
North Carolina Department of Environment
and Natural Resources
450 W. Hanes Mill Rd, Suite 300
Winston Salem, North Carolina 27105
1001 Boulders Parkway P 804.200.6500
Suite 300 F 804.560.1016
Richmond, VA 23225 www.timmons.com
September 26, 2019
Re: N.C. Stream Assessment Method (NC SAM) - Publix Distribution Center - (DWR:
20190289 & USACE: SAW -2018-00240)
Mr. Bailey & Ms. Homewood,
Timmons Group environmental scientists Hunter Wines and Eli Wright conducted a site visit on
September 18, 2019 to perform the N.0 Stream Assessment Method (NC SAM) Evaluation for
the Publix Distribution Center Project (Project) located in Guilford County, NC. The purpose of
this evaluation was to determine the functional assessment ratings for stream channel impacts
associated with the Project. Additionally, this assessment was performed in response to Item 4
in the Additional Information Request dated September 7, 2019 from the USACE. Included in
this letter are the results of the NC SAM evaluation, and proposed mitigation ratios based on the
resulting assessment ratings.
During the evaluation, seven (7) stream reaches were determined to be impaired and were
evaluated using the NC SAM process. Each reach evaluated corresponds to a proposed stream
impact (see Attachment 1: NC SAM Evaluation Map). Attachment 2 includes the NC SAM Field
Assessment Forms and Attachment 3 includes the NC SAM Evaluation Photo Document.
Mitigation ratios for the assessed streams are proposed based on the following criteria: overall
low scores at 1:1, overall medium scores at 1.5:1. Streams that were not evaluated are
assumed to require a 2:1 mitigation ratio. Additionally, all wetland impacts are assumed at a
ratio of 2:1. Attachment 4 includes a summary of the proposed mitigation for the Project.
Table 1 (below) provides a summary of the overall findings of the evaluation:
CIVIL ENGINEERING I ENVIRONMENTAL I SURVEYING I GIS I LANDSCAPE ARCHITECTURE I CONSTRUCTION SERVICES

Please feel free to contact Brian Breissinger at (804)-200-6439, or by email at
brian.breissinger(a)_timmons.com if you have any questions.
Sincerely,
Timmons Group
Brian Breissinger
Environmental Services Manager
Attachments:
1. NC SAM Evaluation Map
2. NC SAM Field Assessment Forms
3. NC SAM Photo Document
4. Proposed Mitigation
Cc (by e-mail):
Jay Matey, PE, Timmons Group
Brian Crutchfield, PE, Timmons Group
Robin Perez, Timmons Group
John Fisher, Publix
CIVIL ENGINEERING I ENVIRONMENTAL I SURVEYING I GIS I LANDSCAPE ARCHITECTURE I CONSTRUCTION SERVICES
Table 1: NC SAM Stream Evaluation Summary
Function Class Rating
Length of
Evaluated Reach
Site Number Stream Impact ID (ft)
Hydrology
Water
Quality
Habitat
Overall
Proposed
Mitigation
Ratio
SAM -S5-1
S5
57
Low
Medium
Low
Low
1:1
SAM -S4-2
S4
283
Medium
Medium
Low
Medium
1.5:1
SAM -S3-3
S3
235
Low
Medium
Low
Low
1:1
SAM -S8-4
S8
26
Low
Low
Medium
Low
1:1
SAM -S2-5
S2
318
Medium
High
Medium
Medium
1.5:1
SAM-S7B-6
S7B
437
Medium
High
Medium
Medium
1.5:1
SAM -SX -7
S7C
55
Low
High
Medium
Medium
1.5:1
Please feel free to contact Brian Breissinger at (804)-200-6439, or by email at
brian.breissinger(a)_timmons.com if you have any questions.
Sincerely,
Timmons Group
Brian Breissinger
Environmental Services Manager
Attachments:
1. NC SAM Evaluation Map
2. NC SAM Field Assessment Forms
3. NC SAM Photo Document
4. Proposed Mitigation
Cc (by e-mail):
Jay Matey, PE, Timmons Group
Brian Crutchfield, PE, Timmons Group
Robin Perez, Timmons Group
John Fisher, Publix
CIVIL ENGINEERING I ENVIRONMENTAL I SURVEYING I GIS I LANDSCAPE ARCHITECTURE I CONSTRUCTION SERVICES

Attachment
NC SAM Evaluation Map

0
r x ao
r
r
Ian Or Qa
Rp
S !
_ ky H', 4r •
Legend
NCSAM Evaluation
Project Limits - 354.2 Acres
r
0
Limits of Disturbance - 231.3 Acres
G. 001
© Stream Impact
Wetland Impact
----- Stream Buffers
Perennial Stream (R3)
Intermittent Stream (R4)
Permanent Stream Impact
Temporary Stream Impact
Secondary Stream Impacts
Stream Top of Bank
Palustrine Forested (PFO) Wetland
I I Palustrine Emergent (PEM) Wetland
Palustrine Open Water (POW)
Wetland Impacts
11111111Secondary Wetland Impacts
NC DOT TIP Project: U-2581 BA - 15.1 Acres
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Attachment 2:
NC SAM Field Assessment Forms

Accompanies User Manual Version 2
t:arcwator version z
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
Manual for detailed descriptions and explanations of requested information. Record in the "Notes/Sketch" section if any supplementary
measurements were performed. Seethe NC SAM User Manual for examples of additional measurements that maybe relevant.
NOTE EVIDENCE OF STRESSORS AFFECTING THE ASSESSMENT AREA (do not need to be within the assessment area).
PROJECT/ SITE INFORMATION:
1. Project name (if any): Public Distribution Center (S5-1) 2. Date of evaluation: 09/19/2019
3. Applicant/owner name: Public Super Markets Inc. 4. Assessor name/organization: E. Wright, H. Wines
5. County: Guilford 6. Nearest named water body
7. River Basin: Cape Fear on USGS 7.5 -minute quad: Little Alamance Creek
8. Site coordinates (decimal degrees, at lower end of assessment reach): 36.0796, -79.6632
STREAM INFORMATION: (depth and width can be approximations)
9. Site number (show on attached map): SAM -S5-1 10. Length of assessment reach evaluated (feet): 57
11. Channel depth from bed (in riffle, if present) to top of bank (feet): 4 r Unable to assess channel depth.
12. Channel width at top of bank (feet): 3 13. Is assessment reach a swamp stream? r Yes r No
14. Feature type: r Perennial flow • Intermittent flow r Tidal Marsh Stream
STREAM RATING INFORMATION:
15. NC SAM Zone: r Mountains (M) {o Piedmont (P) r Inner Coastal Plain (I) r Outer Coastal Plain (0)
16. Estimated geomorphic l 1
valley shape (skip for r 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 mi`) ( Size 2 (0.1 to < 0.5 mi`) r Size 3 (0.5 to < 5 mi`) r Size 4 (>_ 5 mit)
for Tidal Marsh Stream)
ADDITIONAL INFORMATION:
18. Were regulatory considerations evaluated? {o Yes r No If Yes, check all that appy to the assessment area.
r Section 10 water r Classified Trout Waters r Water Supply Watershed ( r I r II r III r IV r V)
r Essential Fish Habitat r Primary Nursery Area r High Quality Waters/Outstanding Resource Waters
r Publicly owned property r NCDWR riparian buffer rule in effect r Nutrient Sensitive Waters
r Anadromous fish r 303(d) List r CAMA Area of Environmental Concern (AEC)
r Documented presence of a federal and/or state listed protected species within the assessment area.
List species:
r 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)
{o A Water throughout assessment reach.
r B No flow, water in pools only.
r C No water in assessment reach.
2. Evidence of Flow Restriction - assessment reach metric
{o 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 ora 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).
r B NotA
3. Feature Pattern - assessment reach metric
{o A A majority of the assessment reach has altered pattern (examples: straightening, modification above or below culvert).
r B NotA.
4. Feature Longitudinal Profile - assessment reach metric
{o 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).
r B NotA
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).
r A < 10% of channel unstable
{o B 10 to 25% of channel unstable
r 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
r A r A Little or no evidence of conditions that adversely affect reference interaction
r B r B Moderate evidence of conditions (examples: berms, levees, down -cutting, aggradation, dredging) that adversely affect
reference interaction (examples: limited streamside area access, disruption offlood flows through streamside area,
leaky or intermittent bulkheads, causeways with floodplain constriction, minor ditching [including mosquito ditching])
{o C (o 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

Water Quality Stressors — assessment reach/intertidal zone metric
Check all that apply.
F A Discolored water in stream or intertidal zone (milky white, blue, unnatural water discoloration, oil sheen, stream foam)
r B Excessive sedimentation (burying of stream features or intertidal zone)
r C Noticeable evidence of pollutant discharges entering the assessment reach and causing a water quality problem
r D Odor (not including natural sulfide odors)
r E Current published or collected data indicating degraded water quality in the assessment reach. Cite source in the "Notes/Sketch"
section.
r F Livestock with access to stream or intertidal zone
r G Excessive algae in stream or intertidal zone
r H Degraded marsh vegetation in the intertidal zone (removal, burning, regular mowing, destruction, etc.)
r I Other: (explain in "Notes/Sketch" section)
r 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 streams, D2 drought or higher is considered a
drought.
r A Drought conditions and no rainfall or rainfall not exceeding 1 inch within the last 48 hours
r B Drought conditions and rainfall exceeding 1 inch within the last 48 hours
{o C No drought conditions
9 Large or Dangerous Stream — assessment reach metric
r Yes {o 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. {o Yes r 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)
F A Multiple aquatic macrophytes and aquatic mosses --F,E r F 5% oysters or other natural hard bottoms
(include liverworts, lichens, and algal mats) F m r G Submerged aquatic vegetation
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r B Multiple sticks and/or leaf packs and/or emergent o r H Low -tide refugia (pools)
vegetation r 0 F I Sand bottom
r C Multiple snags and logs (including lap trees) L r J 5% vertical bank along the marsh
r D 5% undercut banks and/or root mats and/or roots O r K Little or no habitat
in banks extend to the normal wetted perimeter
r E Little or no habitat
*********************************REMAINING QUESTIONS ARE NOT APPLICABLE FOR TIDAL MARSH STREAMS**********************...
11. Bedform and Substrate —assessment reach metric (skip for Size 4 Coastal Plain streams and Tidal Marsh Streams)
Ila. r Yes {o No Is assessment reach in a natural sand -bed stream? (skip for Coastal Plain streams)
11b_ Bedform evaluated. Check the appropriate box(es).
r A Riffle -run section (evaluate 11c)
r B Pool -glide section (evaluate 11d)
r C Natural bedform absent (skip to Metric 12, Aquatic Life)
11 c. 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
r r r r r Bed rock/sa pro lite
r r r r r Boulder (256 — 4096 mm)
r r r r r Cobble (64 — 256 mm)
r r r r r Gravel (2 — 64 mm)
r r r r r Sand (.062 — 2 mm)
r r r r r Silt/clay (< 0.062 mm)
r r r r r Detritus
r r r r r Artificial (rip -rap, concrete, etc.)
11d. r Yes r 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. {o Yes r 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. r No Water r Other:
12b. {o Yes r 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.
r rAdult frogs
r r Aquatic reptiles
r r Aquatic macrophytes and aquatic mosses (include liverworts, lichens, and algal mats)
r r Beetles (including water pennies)
r r Caddisfiy larvae (Trichoptera [T])
r r Asian clam (Corbicula )
r r Crustacean (isopod/a m phipod/crayfish/sh rim p)
r r Damselfly and dragonfly larvae
r r Dipterans (true flies)
r r Mayfly larvae (Ephemeroptera [E])
r r Megaloptera (alderfly, fishily, dobsonfly larvae)
r r Midges/mosquito larvae
r r Mosquito fish (Gambusia) or mud minnows (Umbra pygmaea)

r r Mussels/Clams (not Corbicula )
r r Other fish
r r Salamanders/tadpoles
r r Snails
r r Stonefly larvae (Plecoptera [PI)
r r Tipulid larvae
r r 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
r A r A Little or no alteration to water storage capacity over a majority of the streamside area
r B r B Moderate alteration to water storage capacity over a majority of the streamside area
r C r 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
r A r A Majority of streamside area with depressions able to pond water>_ 6 inches deep
r B r B Majority of streamside area with depressions able to pond water 3 to 6 inches deep
r C r 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
r Y r Y Are wetlands present in the streamside area?
r 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.
r A Streams and/or springs Qurisdictional discharges)
F B Ponds (include wet detention basins; do not include sediment basins or dry detention basins)
r C Obstruction that passes some flow during low -flow periods within assessment area (beaver dam, bottom -release dam)
r D Evidence of bank seepage or sweating (iron oxidizing bacteria in water indicates seepage)
F E Stream bed or bank soil reduced (dig through deposited sediment if present)
r F None of the above
17. Baseflow Detractors — assessment area metric (skip for Tidal Marsh Streams)
Check all that apply.
r A Evidence of substantial water withdrawals from the assessment reach (includes areas excavated for pump installation)
r B Obstruction not passing flow during low flow periods affecting the assessment reach (ex: watertight dam, sediment deposit)
r C Urban stream (>_ 24% impervious surface for watershed)
r D Evidence that the stream -side area has been modified resulting in accelerated drainage into the assessment reach
r E Assessment reach relocated to valley edge
r F None of the above
18. Shading — assessment reach metric (skip for Tidal Marsh Streams)
Consider aspect. Consider "leaf -on" condition.
r A Stream shading is appropriate for stream category (may include gaps associated with natural processes)
{o B Degraded (example: scattered trees)
r 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
{o A r A r A r A > 100 -feet wide or extends to the edge of the watershed
r B r B r B r B From 50 to < 100 -feet wide
r C r C r C r C From 30 to < 50 -feet wide
r D r D r D r D From 10 to < 30 -feet wide
r E r E {t E r 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
r A r A Mature forest
r B r B Non -mature woody vegetation or modified vegetation structure
{o C {o C Herbaceous vegetation with orwithout a strip of trees < 10 feet wide
r D r D Maintained shrubs
r E r 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: r
Abuts < 30 feet 30-50 feet
LB RB LB RB LB RB
r r r r r r Row crops
r B r B r B r B r B r B Maintained turf
r C r C r C r C r C r C Pasture (no livestock)/commercial horticulture
r D r D r D r D r D r 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
r A r A Medium to high stem density
{o B {o B Low stem density
r C r 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
{o A {o A The total length of buffer breaks is < 25 percent.
r B r B The total length of buffer breaks is between 25 and 50 percent.
r C r 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
r A r 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-
r B r 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.
{o C {o 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. r Yes {o No Was a conductivity measurement recorded?
If No, select one of the following reasons. r No Water {o Other: No Meter
25b. Check the box corresponding to the conductivity measurement (units of microsiemens per centimeter).
r A <46 r B 46 to < 67 r C 67 to < 79 r D 79 to < 230 r E >> 230
Notes/Sketch-
See Support Document

Draft NC SAM Stream Rating Sheet
Accompanies User Manual Version 1
Rating Calculator Version 1
Stream Site Name Publix Distribution Center
Stream Category Pb1
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)
Date of Evaluation 09/19/2019
Assessor Name/Organization E. Wright, H. Wines
YES
NO
vGc
intermittent
USACE/
NCDWR
Function Class Rating Summary
All Streams
Intermittent
(1) Hydrology
LOW
LOW
(2) Baseflow
MEDIUM
MEDIUM
(2) Flood Flow
LOW
LOW
(3) Streamside Area Attenuation
LOW
LOW
(4) Floodplain Access
LOW
LOW
(4) Wooded Riparian Buffer
LOW
LOW
(4) Microtopography
NA
NA
(3) Stream Stability
LOW
LOW
(4) Channel Stability
MEDIUM
MEDIUM
(4) Sediment Transport
LOW
LOW
(4) Stream Geomorphology
LOW
LOW
(2) Stream/Intertidal Zone Interaction
NA
NA
(2) Longitudinal Tidal Flow
NA
NA
(2) Tidal Marsh Stream Stability
NA
NA
(3) Tidal Marsh Channel Stability
NA
NA
(3) Tidal Marsh Stream Geomorphology
NA
NA
(1) Water Quality
MEDIUM
MEDIUM
(2) Baseflow
MEDIUM
MEDIUM
(2) Streamside Area Vegetation
MEDIUM
MEDIUM
(3) Upland Pollutant Filtration
MEDIUM
MEDIUM
(3) Thermoregulation
MEDIUM
MEDIUM
(2) Indicators of Stressors
NO
NO
(2) Aquatic Life Tolerance
MEDIUM
NA
(2) Intertidal Zone Filtration
NA
NA
(1) Habitat
LOW
LOW
(2) In -stream Habitat
LOW
LOW
(3) Baseflow
MEDIUM
MEDIUM
(3) Substrate
LOW
LOW
(3) Stream Stability
MEDIUM
MEDIUM
(3) In -stream Habitat
MEDIUM
MEDIUM
(2) Stream -side Habitat
LOW
LOW
(3) Stream -side Habitat
LOW
LOW
(3) Thermoregulation
LOW
LOW
(2) Tidal Marsh In -stream Habitat
NA
NA
(3) Flow Restriction
NA
NA
(3) Tidal Marsh Stream Stability
NA
NA
(4) Tidal Marsh Channel Stability
NA
NA
(4) Tidal Marsh Stream Geomorphology
NA
NA
(3) Tidal Marsh In -stream Habitat
NA
NA
(2) Intertidal Zone Habitat
NA
NA
Overall
LOW
LOW

Accompanies User Manual Version 2
t:arcwator version z
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
Manual for detailed descriptions and explanations of requested information. Record in the "Notes/Sketch" section if any supplementary
measurements were performed. Seethe NC SAM User Manual for examples of additional measurements that maybe relevant.
NOTE EVIDENCE OF STRESSORS AFFECTING THE ASSESSMENT AREA (do not need to be within the assessment area).
PROJECT/ SITE INFORMATION:
1. Project name (if any): Public Distribution Center (S4-2) 2. Date of evaluation: 09/19/2019
3. Applicant/owner name: Public Super Markets Inc. 4. Assessor name/organization: E. Wright, H. Wines
5. County: Guilford 6. Nearest named water body
7. River Basin: Cape Fear on USGS 7.5 -minute quad: Little Alamance Creek
8. Site coordinates (decimal degrees, at lower end of assessment reach): 36.0792, -79.6650
STREAM INFORMATION: (depth and width can be approximations)
9. Site number (show on attached map): SAM -S4-2 10. Length of assessment reach evaluated (feet): 283
11. Channel depth from bed (in riffle, if present) to top of bank (feet): 1 r Unable to assess channel depth.
12. Channel width at top of bank (feet): 3 13. Is assessment reach a swamp stream? r Yes r No
14. Feature type: r Perennial flow • Intermittent flow r Tidal Marsh Stream
STREAM RATING INFORMATION:
15. NC SAM Zone: r Mountains (M) {o Piedmont (P) r Inner Coastal Plain (I) r Outer Coastal Plain (0)
16. Estimated geomorphic l 1
valley shape (skip for r 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 mi`) ( Size 2 (0.1 to < 0.5 mi`) r Size 3 (0.5 to < 5 mi`) r Size 4 (>_ 5 mit)
for Tidal Marsh Stream)
ADDITIONAL INFORMATION:
18. Were regulatory considerations evaluated? {o Yes r No If Yes, check all that appy to the assessment area.
r Section 10 water r Classified Trout Waters r Water Supply Watershed ( r I r II r III r IV r V)
r Essential Fish Habitat r Primary Nursery Area r High Quality Waters/Outstanding Resource Waters
r Publicly owned property r NCDWR riparian buffer rule in effect r Nutrient Sensitive Waters
r Anadromous fish r 303(d) List r CAMA Area of Environmental Concern (AEC)
r Documented presence of a federal and/or state listed protected species within the assessment area.
List species:
r 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)
r A Water throughout assessment reach.
{o B No flow, water in pools only.
r C No water in assessment reach.
2. Evidence of Flow Restriction - assessment reach metric
{o 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 ora 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).
r B NotA
3. Feature Pattern - assessment reach metric
r A A majority of the assessment reach has altered pattern (examples: straightening, modification above or below culvert).
{o B NotA.
4. Feature Longitudinal Profile - assessment reach metric
r 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).
{o B NotA
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).
{o A < 10% of channel unstable
r B 10 to 25% of channel unstable
r 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
r A r A Little or no evidence of conditions that adversely affect reference interaction
r B r B Moderate evidence of conditions (examples: berms, levees, down -cutting, aggradation, dredging) that adversely affect
reference interaction (examples: limited streamside area access, disruption offlood flows through streamside area,
leaky or intermittent bulkheads, causeways with floodplain constriction, minor ditching [including mosquito ditching])
{o C (o 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

Water Quality Stressors — assessment reach/intertidal zone metric
Check all that apply.
r A Discolored water in stream or intertidal zone (milky white, blue, unnatural water discoloration, oil sheen, stream foam)
F B Excessive sedimentation (burying of stream features or intertidal zone)
r C Noticeable evidence of pollutant discharges entering the assessment reach and causing a water quality problem
r D Odor (not including natural sulfide odors)
r E Current published or collected data indicating degraded water quality in the assessment reach. Cite source in the "Notes/Sketch"
section.
r F Livestock with access to stream or intertidal zone
r G Excessive algae in stream or intertidal zone
r H Degraded marsh vegetation in the intertidal zone (removal, burning, regular mowing, destruction, etc.)
r I Other: (explain in "Notes/Sketch" section)
r 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 streams, D2 drought or higher is considered a
drought.
r A Drought conditions and no rainfall or rainfall not exceeding 1 inch within the last 48 hours
r B Drought conditions and rainfall exceeding 1 inch within the last 48 hours
{o C No drought conditions
9 Large or Dangerous Stream — assessment reach metric
r Yes {o 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. {o Yes r 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)
r A Multiple aquatic macrophytes and aquatic mosses --F,E r F 5% oysters or other natural hard bottoms
(include liverworts, lichens, and algal mats) F m r G Submerged aquatic vegetation
a�
r B Multiple sticks and/or leaf packs and/or emergent o r H Low -tide refugia (pools)
vegetation r 0 F I Sand bottom
r C Multiple snags and logs (including lap trees) L r J 5% vertical bank along the marsh
r D 5% undercut banks and/or root mats and/or roots O r K Little or no habitat
in banks extend to the normal wetted perimeter
r E Little or no habitat
*********************************REMAINING QUESTIONS ARE NOT APPLICABLE FOR TIDAL MARSH STREAMS**********************...
11. Bedform and Substrate —assessment reach metric (skip for Size 4 Coastal Plain streams and Tidal Marsh Streams)
1 la. r Yes {o No Is assessment reach in a natural sand -bed stream? (skip for Coastal Plain streams)
11 b. Bedform evaluated. Check the appropriate box(es).
F A Riffle -run section (evaluate 11c)
F B Pool -glide section (evaluate 11d)
r C Natural bedform absent (skip to Metric 12, Aquatic Life)
11 c. 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
{o r r r r Bedrock/sa pro lite
{o r r r r Boulder (256 — 4096 mm)
{o r r r r Cobble (64 — 256 mm)
r r r r {o Gravel (2 — 64 mm)
r r r r r Sand (.062 — 2 mm)
r r {o r r Silt/clay (< 0.062 mm)
{o r r r r Detritus
{o r r r r Artificial (rip -rap, concrete, etc.)
1 ld. r Yes {o 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. {o Yes r 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. r No Water r Other:
12b. {o Yes r 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.
r rAdult frogs
r r Aquatic reptiles
r r Aquatic macrophytes and aquatic mosses (include liverworts, lichens, and algal mats)
r r Beetles (including water pennies)
r r Caddisfly larvae (Trichoptera [T])
r r Asian clam (Corbicula )
r r Crustacean (isopod/a m phipod/crayfish/sh rim p)
r r Damselfly and dragonfly larvae
r r Dipterans (true flies)
r r Mayfly larvae (Ephemeroptera [E])
r r Megaloptera (alderfly, fishily, dobsonfly larvae)
r r Midges/mosquito larvae
r r Mosquito fish (Gambusia) or mud minnows (Umbra pygmaea)

r r Mussels/Clams (not Corbicula )
r r Other fish
r r Salamanders/tadpoles
r r Snails
r r Stonefly larvae (Plecoptera [PI)
r r Tipulid larvae
r r 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
r A r A Little or no alteration to water storage capacity over a majority of the streamside area
r B r B Moderate alteration to water storage capacity over a majority of the streamside area
r C r 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
r A r A Majority of streamside area with depressions able to pond water>_ 6 inches deep
r B r B Majority of streamside area with depressions able to pond water 3 to 6 inches deep
r C r 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
r Y r Y Are wetlands present in the streamside area?
r N r
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.
r A Streams and/or springs Qurisdictional discharges)
F B Ponds (include wet detention basins; do not include sediment basins or dry detention basins)
r C Obstruction that passes some flow during low -flow periods within assessment area (beaver dam, bottom -release dam)
r D Evidence of bank seepage or sweating (iron oxidizing bacteria in water indicates seepage)
F E Stream bed or bank soil reduced (dig through deposited sediment if present)
r F None of the above
17. Baseflow Detractors — assessment area metric (skip for Tidal Marsh Streams)
Check all that apply.
r A Evidence of substantial water withdrawals from the assessment reach (includes areas excavated for pump installation)
r B Obstruction not passing flow during low flow periods affecting the assessment reach (ex: watertight dam, sediment deposit)
r C Urban stream (>_ 24% impervious surface for watershed)
r D Evidence that the stream -side area has been modified resulting in accelerated drainage into the assessment reach
r E Assessment reach relocated to valley edge
r F None of the above
18. Shading — assessment reach metric (skip for Tidal Marsh Streams)
Consider aspect. Consider "leaf -on" condition.
{o A Stream shading is appropriate for stream category (may include gaps associated with natural processes)
r B Degraded (example: scattered trees)
r 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
{o A r A r A r A > 100 -feet wide or extends to the edge of the watershed
r B r B r B r B From 50 to < 100 -feet wide
r C r C r C r C From 30 to < 50 -feet wide
r D r D {o D r D From 10 to < 30 -feet wide
r E r E r E r 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
r A r A Mature forest
r B r B Non -mature woody vegetation or modified vegetation structure
{o C {o C Herbaceous vegetation with orwithout a strip of trees < 10 feet wide
r D r D Maintained shrubs
r E r 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: r
Abuts < 30 feet 30-50 feet
LB RB LB RB LB RB
r r r r r r Row crops
r B r B r B r B r B r B Maintained turf
r C r C r C r C r C r C Pasture (no livestock)/commercial horticulture
r D r D r D r D r D r 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
{o A {o A Medium to high stem density
r B r B Low stem density
r C r 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
{o A {o A The total length of buffer breaks is < 25 percent.
r B r B The total length of buffer breaks is between 25 and 50 percent.
r C r 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
r A r 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.
{t B r 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.
r C {o 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. r Yes {o No Was a conductivity measurement recorded?
If No, select one of the following reasons. r No Water {o Other: No Meter
25b. Check the box corresponding to the conductivity measurement (units of microsiemens per centimeter).
r A <46 r B 46 to < 67 r C 67 to < 79 r D 79 to < 230 r E >> 230
Notes/Sketch-
see Support Document

Draft NC SAM Stream Rating Sheet
Accompanies User Manual Version 1
Rating Calculator Version 1
Stream Site Name Publix Distribution Center
Stream Category Pb1
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)
Date of Evaluation 09/19/2019
Assessor Name/Organization E. Wright, H. Wines
YES
NO
vGc
intermittent
USACE/
NCDWR
Function Class Rating Summary
All Streams
Intermittent
(1) Hydrology
MEDIUM
MEDIUM
(2) Baseflow
MEDIUM
MEDIUM
(2) Flood Flow
MEDIUM
MEDIUM
(3) Streamside Area Attenuation
LOW
LOW
(4) Floodplain Access
LOW
LOW
(4) Wooded Riparian Buffer
LOW
LOW
(4) Microtopography
NA
NA
(3) Stream Stability
HIGH
HIGH
(4) Channel Stability
HIGH
HIGH
(4) Sediment Transport
MEDIUM
MEDIUM
(4) Stream Geomorphology
HIGH
HIGH
(2) Stream/Intertidal Zone Interaction
NA
NA
(2) Longitudinal Tidal Flow
NA
NA
(2) Tidal Marsh Stream Stability
NA
NA
(3) Tidal Marsh Channel Stability
NA
NA
(3) Tidal Marsh Stream Geomorphology
NA
NA
(1) Water Quality
MEDIUM
MEDIUM
(2) Baseflow
MEDIUM
MEDIUM
(2) Streamside Area Vegetation
HIGH
HIGH
(3) Upland Pollutant Filtration
HIGH
HIGH
(3) Thermoregulation
HIGH
HIGH
(2) Indicators of Stressors
NO
NO
(2) Aquatic Life Tolerance
LOW
NA
(2) Intertidal Zone Filtration
NA
NA
(1) Habitat
LOW
LOW
(2) In -stream Habitat
LOW
MEDIUM
(3) Baseflow
MEDIUM
MEDIUM
(3) Substrate
MEDIUM
MEDIUM
(3) Stream Stability
HIGH
HIGH
(3) In -stream Habitat
LOW
MEDIUM
(2) Stream -side Habitat
LOW
LOW
(3) Stream -side Habitat
LOW
LOW
(3) Thermoregulation
MEDIUM
MEDIUM
(2) Tidal Marsh In -stream Habitat
NA
NA
(3) Flow Restriction
NA
NA
(3) Tidal Marsh Stream Stability
NA
NA
(4) Tidal Marsh Channel Stability
NA
NA
(4) Tidal Marsh Stream Geomorphology
NA
NA
(3) Tidal Marsh In -stream Habitat
NA
NA
(2) Intertidal Zone Habitat
NA
NA
Overall
MEDIUM
MEDIUM

Accompanies User Manual Version 2
t:arcwator version z
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
Manual for detailed descriptions and explanations of requested information. Record in the "Notes/Sketch" section if any supplementary
measurements were performed. Seethe NC SAM User Manual for examples of additional measurements that maybe relevant.
NOTE EVIDENCE OF STRESSORS AFFECTING THE ASSESSMENT AREA (do not need to be within the assessment area).
PROJECT/ SITE INFORMATION:
1. Project name (if any): Public Distribution Center (S3-3) 2. Date of evaluation: 09/19/2019
3. Applicant/owner name: Public Super Markets Inc. 4. Assessor name/organization: E. Wright, H. Wines
5. County: Guilford 6. Nearest named water body
7. River Basin: Cape Fear on USGS 7.5 -minute quad: Little Alamance Creek
8. Site coordinates (decimal degrees, at lower end of assessment reach): 36.0787, -79.6656
STREAM INFORMATION: (depth and width can be approximations)
9. Site number (show on attached map): SAM -S3-3 10. Length of assessment reach evaluated (feet): 235
11. Channel depth from bed (in riffle, if present) to top of bank (feet): 5 r Unable to assess channel depth.
12. Channel width at top of bank (feet): 6 13. Is assessment reach a swamp stream? r Yes r No
14. Feature type: r Perennial flow • Intermittent flow r Tidal Marsh Stream
STREAM RATING INFORMATION:
15. NC SAM Zone: r Mountains (M) (o Piedmont (P) r Inner Coastal Plain (I) r Outer Coastal Plain (0)
16. Estimated geomorphic l 1
valley shape (skip for r 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 mi`) ( Size 2 (0.1 to < 0.5 mi`) r Size 3 (0.5 to < 5 mi`) r Size 4 (>_ 5 mit)
for Tidal Marsh Stream)
ADDITIONAL INFORMATION:
18. Were regulatory considerations evaluated? (o Yes r No If Yes, check all that appy to the assessment area.
r Section 10 water r Classified Trout Waters r Water Supply Watershed ( r I r II r III r IV r V)
r Essential Fish Habitat r Primary Nursery Area r High Quality Waters/Outstanding Resource Waters
r Publicly owned property r NCDWR riparian buffer rule in effect r Nutrient Sensitive Waters
r Anadromous fish r 303(d) List r CAMA Area of Environmental Concern (AEC)
r Documented presence of a federal and/or state listed protected species within the assessment area.
List species:
r 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)
r A Water throughout assessment reach.
r B No flow, water in pools only.
(o 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 NotA
3. Feature Pattern - assessment reach metric
( A A majority of the assessment reach has altered pattern (examples: straightening, modification above or below culvert).
{: B NotA.
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 NotA
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
r A r A Little or no evidence of conditions that adversely affect reference interaction
r B r B Moderate evidence of conditions (examples: berms, levees, down -cutting, aggradation, dredging) that adversely affect
reference interaction (examples: limited streamside area access, disruption offlood flows through streamside area,
leaky or intermittent bulkheads, causeways with floodplain constriction, minor ditching [including mosquito ditching])
(o C (o 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

Water Quality Stressors — assessment reach/intertidal zone metric
Check all that apply.
r A Discolored water in stream or intertidal zone (milky white, blue, unnatural water discoloration, oil sheen, stream foam)
r B Excessive sedimentation (burying of stream features or intertidal zone)
r C Noticeable evidence of pollutant discharges entering the assessment reach and causing a water quality problem
r D Odor (not including natural sulfide odors)
r E Current published or collected data indicating degraded water quality in the assessment reach. Cite source in the "Notes/Sketch"
section.
r F Livestock with access to stream or intertidal zone
r G Excessive algae in stream or intertidal zone
r H Degraded marsh vegetation in the intertidal zone (removal, burning, regular mowing, destruction, etc.)
r I Other (explain in "Notes/Sketch" section)
F 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 or4 streams, D2 drought or higher is considered a
drought.
r A Drought conditions and no rainfall or rainfall not exceeding 1 inch within the last 48 hours
r B Drought conditions and rainfall exceeding 1 inch within the last 48 hours
fo C No drought conditions
9 Large or Dangerous Stream - assessment reach metric
r Yes fo 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. fo Yes r 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)
r A Multiple aquatic macrophytes and aquatic mosses --F,E r F 5% oysters or other natural hard bottoms
(include liverworts, lichens, and algal mats) F m r G Submerged aquatic vegetation
a�
r B Multiple sticks and/or leaf packs and/or emergent o r H Low -tide refugia (pools)
vegetation Y L c r l Sand bottom
r C Multiple snags and logs (including lap trees) L r J 5% vertical bank along the marsh
r D 5% undercut banks and/or root mats and/or roots O r K Little or no habitat
in banks extend to the normal wetted perimeter
r E Little or no habitat
*********************************REMAINING QUESTIONS ARE NOT APPLICABLE FOR TIDAL MARSH STREAMS**********************...
11. Bedform and Substrate -assessment reach metric (skip for Size 4 Coastal Plain streams and Tidal Marsh Streams)
Ila. r Yes fo No Is assessment reach in a natural sand -bed stream? (skip for Coastal Plain streams)
11 b. Bedform evaluated. Check the appropriate box(es).
F A Riffle -run section (evaluate 11c)
r B Pool -glide section (evaluate 11d)
r C Natural bedform absent (skip to Metric 12, Aquatic Life)
11 c. 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
r fo r r r Bedrock/sa pro lite
fo r r r r Boulder (256 - 4096 mm)
r r [+ r r Cobble (64 - 256 mm)
fo r r r r Gravel (2 - 64 mm)
f-' fo r r r Sand (.062 - 2 mm)
f-' r r fo r Silt/clay (< 0.062 mm)
f-' fo r r r Detritus
f-' r fo r r Artificial (rip -rap, concrete, etc.)
11d. r Yes r 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. fo Yes r 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. r No Water r Other:
12b. r Yes fo 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.
r rAdult frogs
r r Aquatic reptiles
r r Aquatic macrophytes and aquatic mosses (include liverworts, lichens, and algal mats)
r r Beetles (including water pennies)
r r Caddisfiy larvae (Trichoptera [T])
r r Asian clam (Corbicula )
r r Crustacean (isopod/amphipod/crayfish/sh rim p)
r r Damselfly and dragonfly larvae
r r Dipterans (true flies)
r r Mayfly larvae (Ephemeroptera [E])
r r Megaloptera (alderfly, fshfly, dobsonfly larvae)
r r Midges/mosquito larvae
r r Mosquito fish (Gambusia) or mud minnows (Umbra pygmaea)

r r Mussels/Clams (not Corbicula )
r r Other fish
r r Salamanders/tadpoles
r r Snails
r r Stonefly larvae (Plecoptera [P])
r r Tipulid larvae
r r 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
r A r A Little or no alteration to water storage capacity over a majority of the streamside area
r B r B Moderate alteration to water storage capacity over a majority of the streamside area
r C r 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
r A r A Majority of streamside area with depressions able to pond water>_ 6 inches deep
r B r B Majority of streamside area with depressions able to pond water 3 to 6 inches deep
r C r 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
r Y (- Y Are wetlands present in the streamside area?
rN (oN
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.
r A Streams and/or springs Qurisdictional discharges)
r B Ponds (include wet detention basins; do not include sediment basins or dry detention basins)
r C Obstruction that passes some flow during low -flow periods within assessment area (beaver dam, bottom -release dam)
r D Evidence of bank seepage or sweating (iron oxidizing bacteria in water indicates seepage)
F E Stream bed or bank soil reduced (dig through deposited sediment if present)
r F None of the above
17. Baseflow Detractors - assessment area metric (skip for Tidal Marsh Streams)
Check all that apply.
r A Evidence of substantial water withdrawals from the assessment reach (includes areas excavated for pump installation)
r B Obstruction not passing flow during low flow periods affecting the assessment reach (ex: watertight dam, sediment deposit)
r C Urban stream (>_ 24% impervious surface for watershed)
r D Evidence that the stream -side area has been modified resulting in accelerated drainage into the assessment reach
r E Assessment reach relocated to valley edge
r 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
r A (o A Mature forest
r B r B Non -mature woody vegetation or modified vegetation structure
(o C r C Herbaceous vegetation with orwithout a strip of trees < 10 feet wide
r D r D Maintained shrubs
r E r 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: r
Abuts < 30 feet 30-50 feet
LB RB LB RB LB RB
("'A ("'A ("'A ("'A ("'A ("'A Row crops
r B r B r B r B r B r B Maintained turf
r C r C r C r C r C r C Pasture (no livestock)/commercial horticulture
r D r D r D r D r D r 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
r A {o A Medium to high stem density
{o B r B Low stem density
r C r 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
{o A {o A The total length of buffer breaks is < 25 percent.
r B r B The total length of buffer breaks is between 25 and 50 percent.
r C r 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
r A r 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-
r B {o 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.
f+ C r 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. r Yes {o No Was a conductivity measurement recorded?
If No, select one of the following reasons. {o No Water r Other:
25b. Check the box corresponding to the conductivity measurement (units of microsiemens per centimeter).
r A <46 r B 46 to < 67 r C 67 to < 79 r D 79 to < 230 r E >> 230
Notes/Sketch-
see Support Document

Draft NC SAM Stream Rating Sheet
Accompanies User Manual Version 1
Rating Calculator Version 1
Stream Site Name Publix Distribution Center
Stream Category Pb1
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)
Date of Evaluation 09/19/2019
Assessor Name/Organization E. Wright, H. Wines
YES
NO
vGc
intermittent
USACE/
NCDWR
Function Class Rating Summary
All Streams
Intermittent
(1) Hydrology
LOW
LOW
(2) Baseflow
MEDIUM
MEDIUM
(2) Flood Flow
LOW
LOW
(3) Streamside Area Attenuation
LOW
LOW
(4) Floodplain Access
LOW
LOW
(4) Wooded Riparian Buffer
MEDIUM
MEDIUM
(4) Microtopography
NA
NA
(3) Stream Stability
LOW
LOW
(4) Channel Stability
LOW
LOW
(4) Sediment Transport
LOW
LOW
(4) Stream Geomorphology
MEDIUM
MEDIUM
(2) Stream/Intertidal Zone Interaction
NA
NA
(2) Longitudinal Tidal Flow
NA
NA
(2) Tidal Marsh Stream Stability
NA
NA
(3) Tidal Marsh Channel Stability
NA
NA
(3) Tidal Marsh Stream Geomorphology
NA
NA
(1) Water Quality
MEDIUM
MEDIUM
(2) Baseflow
MEDIUM
MEDIUM
(2) Streamside Area Vegetation
MEDIUM
MEDIUM
(3) Upland Pollutant Filtration
MEDIUM
MEDIUM
(3) Thermoregulation
HIGH
HIGH
(2) Indicators of Stressors
NO
NO
(2) Aquatic Life Tolerance
OMITTED
NA
(2) Intertidal Zone Filtration
NA
NA
(1) Habitat
LOW
LOW
(2) In -stream Habitat
LOW
LOW
(3) Baseflow
MEDIUM
MEDIUM
(3) Substrate
LOW
LOW
(3) Stream Stability
LOW
LOW
(3) In -stream Habitat
MEDIUM
MEDIUM
(2) Stream -side Habitat
MEDIUM
MEDIUM
(3) Stream -side Habitat
LOW
LOW
(3) Thermoregulation
HIGH
HIGH
(2) Tidal Marsh In -stream Habitat
NA
NA
(3) Flow Restriction
NA
NA
(3) Tidal Marsh Stream Stability
NA
NA
(4) Tidal Marsh Channel Stability
NA
NA
(4) Tidal Marsh Stream Geomorphology
NA
NA
(3) Tidal Marsh In -stream Habitat
NA
NA
(2) Intertidal Zone Habitat
NA
NA
Overall
LOW
LOW

Accompanies User Manual Version 2
t:arcwator version z
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
Manual for detailed descriptions and explanations of requested information. Record in the "Notes/Sketch" section if any supplementary
measurements were performed. Seethe NC SAM User Manual for examples of additional measurements that maybe relevant.
NOTE EVIDENCE OF STRESSORS AFFECTING THE ASSESSMENT AREA (do not need to be within the assessment area).
PROJECT/ SITE INFORMATION:
1. Project name (if any): Public Distribution Center (S8-4) 2. Date of evaluation: 09/19/2019
3. Applicant/owner name: Public Super Markets Inc. 4. Assessor name/organization: E. Wright, H. Wines
5. County: Guilford 6. Nearest named water body
7. River Basin: Cape Fear on USGS 7.5 -minute quad: Little Alamance Creek
8. Site coordinates (decimal degrees, at lower end of assessment reach): 36.0785, -79.6660
STREAM INFORMATION: (depth and width can be approximations)
9. Site number (show on attached map): SAM -S8-4 10. Length of assessment reach evaluated (feet): 26
11. Channel depth from bed (in riffle, if present) to top of bank (feet): 5 r Unable to assess channel depth.
12. Channel width at top of bank (feet): 6 13. Is assessment reach a swamp stream? r Yes r No
14. Feature type: r Perennialflow r Intermittent flow r Tidal Marsh Stream
STREAM RATING INFORMATION:
15. NC SAM Zone: r Mountains (M) {o Piedmont (P) r Inner Coastal Plain (I) r Outer Coastal Plain (0)
16. Estimated geomorphic l 1
valley shape (skip for {o a �`�'- r b
Tidal Marsh Stream): (more sinuous stream, flatter valley slope) (less sinuous stream, steeper valley slope)
17. Watershed size: (skip ( Size 1 (< 0.1 mi`) ( Size 2 (0.1 to < 0.5 mi`) (o Size 3 (0.5 to < 5 mi`) r Size 4 (>_ 5 mit)
for Tidal Marsh Stream)
ADDITIONAL INFORMATION:
18. Were regulatory considerations evaluated? {o Yes r No If Yes, check all that appy to the assessment area.
r Section 10 water r Classified Trout Waters r Water Supply Watershed ( r I r II r III r IV r V)
r Essential Fish Habitat r Primary Nursery Area r High Quality Waters/Outstanding Resource Waters
r Publicly owned property r NCDWR riparian buffer rule in effect r Nutrient Sensitive Waters
r Anadromous fish r 303(d) List r CAMA Area of Environmental Concern (AEC)
r Documented presence of a federal and/or state listed protected species within the assessment area.
List species:
r 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)
r A Water throughout assessment reach.
{o B No flow, water in pools only.
r C No water in assessment reach.
2. Evidence of Flow Restriction - assessment reach metric
r 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).
{o B NotA
3. Feature Pattern - assessment reach metric
r A A majority of the assessment reach has altered pattern (examples: straightening, modification above or below culvert).
{o B NotA.
4. Feature Longitudinal Profile - assessment reach metric
{o 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).
r B NotA
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).
r A < 10% of channel unstable
r B 10 to 25% of channel unstable
{o 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
r A r A Little or no evidence of conditions that adversely affect reference interaction
r B r B Moderate evidence of conditions (examples: berms, levees, down -cutting, aggradation, dredging) that adversely affect
reference interaction (examples: limited streamside area access, disruption offlood flows through streamside area,
leaky or intermittent bulkheads, causeways with floodplain constriction, minor ditching [including mosquito ditching])
{o C r 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

Water Quality Stressors — assessment reach/intertidal zone metric
Check all that apply.
r A Discolored water in stream or intertidal zone (milky white, blue, unnatural water discoloration, oil sheen, stream foam)
F B Excessive sedimentation (burying of stream features or intertidal zone)
r C Noticeable evidence of pollutant discharges entering the assessment reach and causing a water quality problem
r D Odor (not including natural sulfide odors)
r E Current published or collected data indicating degraded water quality in the assessment reach. Cite source in the "Notes/Sketch"
section.
r F Livestock with access to stream or intertidal zone
r G Excessive algae in stream or intertidal zone
r H Degraded marsh vegetation in the intertidal zone (removal, burning, regular mowing, destruction, etc.)
r I Other: (explain in "Notes/Sketch" section)
r 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 streams, D2 drought or higher is considered a
drought.
r A Drought conditions and no rainfall or rainfall not exceeding 1 inch within the last 48 hours
r B Drought conditions and rainfall exceeding 1 inch within the last 48 hours
{o C No drought conditions
9 Large or Dangerous Stream — assessment reach metric
r Yes {o 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. {o Yes r 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)
r A Multiple aquatic macrophytes and aquatic mosses --F,E r F 5% oysters or other natural hard bottoms
(include liverworts, lichens, and algal mats) F m r G Submerged aquatic vegetation
a�
r B Multiple sticks and/or leaf packs and/or emergent o r H Low -tide refugia (pools)
vegetation r 0 F I Sand bottom
r C Multiple snags and logs (including lap trees) L r J 5% vertical bank along the marsh
r D 5% undercut banks and/or root mats and/or roots O r K Little or no habitat
in banks extend to the normal wetted perimeter
r E Little or no habitat
*********************************REMAINING QUESTIONS ARE NOT APPLICABLE FOR TIDAL MARSH STREAMS**********************...
11. Bedform and Substrate —assessment reach metric (skip for Size 4 Coastal Plain streams and Tidal Marsh Streams)
11a. {o Yes r No Is assessment reach in a natural sand -bed stream? (skip for Coastal Plain streams)
11 b. Bedform evaluated. Check the appropriate box(es).
F A Riffle -run section (evaluate 11c)
F B Pool -glide section (evaluate 11d)
r C Natural bedform absent (skip to Metric 12, Aquatic Life)
11 c. 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
{o r r r r Bedrock/sa pro lite
{o r r r r Boulder (256 — 4096 mm)
r r {o r r Cobble (64 — 256 mm)
r r r r r Gravel (2 — 64 mm)
r r {o r r Sand (.062 — 2 mm)
r r r r r Silt/clay (< 0.062 mm)
r r r r r Detritus
{o r r r r Artificial (rip -rap, concrete, etc.)
1 ld. r Yes {o 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. {o Yes r 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. r No Water r Other:
12b. {o Yes r 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.
r FAdult frogs
r r Aquatic reptiles
r r Aquatic macrophytes and aquatic mosses (include liverworts, lichens, and algal mats)
r r Beetles (including water pennies)
r r Caddisfly larvae (Trichoptera [T])
r r Asian clam (Corbicula )
r r Crustacean (isopod/a m phipod/crayfish/sh rim p)
r r Damselfly and dragonfly larvae
r r Dipterans (true flies)
r r Mayfly larvae (Ephemeroptera [E])
r r Megaloptera (alderfly, fishily, dobsonfly larvae)
r r Midges/mosquito larvae
r r Mosquito fish (Gambusia) or mud minnows (Umbra pygmaea)

r r Mussels/Clams (not Corbicula )
r r Other fish
r r Salamanders/tadpoles
r r Snails
r r Stonefly larvae (Plecoptera [PI)
r r Tipulid larvae
r r 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
r A r A Little or no alteration to water storage capacity over a majority of the streamside area
r B r B Moderate alteration to water storage capacity over a majority of the streamside area
{o C r 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
r A r A Majority of streamside area with depressions able to pond water>_ 6 inches deep
r B r B Majority of streamside area with depressions able to pond water 3 to 6 inches deep
{o C r 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
r Y r Y Are wetlands present in the streamside area?
r 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.
r A Streams and/or springs Qurisdictional discharges)
r B Ponds (include wet detention basins; do not include sediment basins or dry detention basins)
F C Obstruction that passes some flow during low -flow periods within assessment area (beaver dam, bottom -release dam)
r D Evidence of bank seepage or sweating (iron oxidizing bacteria in water indicates seepage)
F E Stream bed or bank soil reduced (dig through deposited sediment if present)
r F None of the above
17. Baseflow Detractors — assessment area metric (skip for Tidal Marsh Streams)
Check all that apply.
r A Evidence of substantial water withdrawals from the assessment reach (includes areas excavated for pump installation)
r B Obstruction not passing flow during low flow periods affecting the assessment reach (ex: watertight dam, sediment deposit)
r C Urban stream (>_ 24% impervious surface for watershed)
r D Evidence that the stream -side area has been modified resulting in accelerated drainage into the assessment reach
r E Assessment reach relocated to valley edge
r F None of the above
18. Shading — assessment reach metric (skip for Tidal Marsh Streams)
Consider aspect. Consider "leaf -on" condition.
r A Stream shading is appropriate for stream category (may include gaps associated with natural processes)
r B Degraded (example: scattered trees)
{o 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
{o A r A r A r A > 100 -feet wide or extends to the edge of the watershed
r B r B r B r B From 50 to < 100 -feet wide
r C r C r C r C From 30 to < 50 -feet wide
r D r D r D r D From 10 to < 30 -feet wide
r E r E {t E r 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
r A r A Mature forest
r B r B Non -mature woody vegetation or modified vegetation structure
{o C {o C Herbaceous vegetation with orwithout a strip of trees < 10 feet wide
r D r D Maintained shrubs
r E r 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: r
Abuts < 30 feet 30-50 feet
LB RB LB RB LB RB
r r r r r r Row crops
r B r B r B r B r B r B Maintained turf
r C r C r C r C r C r C Pasture (no livestock)/commercial horticulture
r D r D r D r D r D r 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
r A r A Medium to high stem density
r B r B Low stem density
{o C {o 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
{o A {o A The total length of buffer breaks is < 25 percent.
r B r B The total length of buffer breaks is between 25 and 50 percent.
r C r 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
r A r 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-
r B r 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.
{o C {o 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. r Yes {o No Was a conductivity measurement recorded?
If No, select one of the following reasons. r No Water {o Other: No Meter
25b. Check the box corresponding to the conductivity measurement (units of microsiemens per centimeter).
r A <46 r B 46 to < 67 r C 67 to < 79 r D 79 to < 230 r E >> 230
Notes/Sketch-
see Support Document

Draft NC SAM Stream Rating Sheet
Accompanies User Manual Version 1
Rating Calculator Version 1
Stream Site Name Publix Distribution Center
Stream Category Pa3
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)
Function Class Ratin
Date of Evaluation
09/19/2019
Assessor Name/Organization
E. Wright, H. Wines
(2) Flood Flow
LOW
YES
LOW
YES
LOW
YES
LOW
Perennial
USACE/
NCDWR
All Streams
Intermittent
(1) Hydrology
LOW
(2) Baseflow
MEDIUM
(2) Flood Flow
LOW
(3) Streamside Area Attenuation
LOW
(4) Floodplain Access
LOW
(4) Wooded Riparian Buffer
LOW
(4) Microtopography
LOW
(3) Stream Stability
MEDIUM
(4) Channel Stability
LOW
(4) Sediment Transport
HIGH
(4) Stream Geomorphology
MEDIUM
(2) Stream/Intertidal Zone Interaction
NA
(2) Longitudinal Tidal Flow
NA
(2) Tidal Marsh Stream Stability
NA
(3) Tidal Marsh Channel Stability
NA
(3) Tidal Marsh Stream Geomorphology
NA
(1) Water Quality
LOW
(2) Baseflow
MEDIUM
(2) Streamside Area Vegetation
LOW
(3) Upland Pollutant Filtration
MEDIUM
(3) Thermoregulation
LOW
(2) Indicators of Stressors
YES
(2) Aquatic Life Tolerance
MEDIUM
(2) Intertidal Zone Filtration
NA
(1) Habitat
MEDIUM
(2) In -stream Habitat
HIGH
(3) Baseflow
MEDIUM
(3) Substrate
HIGH
(3) Stream Stability
LOW
(3) In -stream Habitat
HIGH
(2) Stream -side Habitat
LOW
(3) Stream -side Habitat
LOW
(3) Thermoregulation
LOW
(2) Tidal Marsh In -stream Habitat
NA
(3) Flow Restriction
NA
(3) Tidal Marsh Stream Stability
NA
(4) Tidal Marsh Channel Stability
NA
(4) Tidal Marsh Stream Geomorphology
NA
(3) Tidal Marsh In -stream Habitat
NA
(2) Intertidal Zone Habitat
NA
Overall
LOW

Accompanies User Manual Version 2
t:arcwator version z
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
Manual for detailed descriptions and explanations of requested information. Record in the "Notes/Sketch" section if any supplementary
measurements were performed. Seethe NC SAM User Manual for examples of additional measurements that maybe relevant.
NOTE EVIDENCE OF STRESSORS AFFECTING THE ASSESSMENT AREA (do not need to be within the assessment area).
PROJECT/ SITE INFORMATION:
1. Project name (if any): Public Distribution Center (S2-5) 2. Date of evaluation: 09/19/2019
3. Applicant/owner name: Public Super Markets Inc. 4. Assessor name/organization: E. Wright, H. Wines
5. County: Guilford 6. Nearest named water body
7. River Basin: Cape Fear on USGS 7.5 -minute quad: Little Alamance Creek
8. Site coordinates (decimal degrees, at lower end of assessment reach): 36.0807, -79.6646
STREAM INFORMATION: (depth and width can be approximations)
9. Site number (show on attached map): SAM -S2-5 10. Length of assessment reach evaluated (feet): 318
11. Channel depth from bed (in riffle, if present) to top of bank (feet): 0.5 r Unable to assess channel depth.
12. Channel width at top of bank (feet): 3 13. Is assessment reach a swamp stream? r Yes r No
14. Feature type: r Perennial flow • Intermittent flow r Tidal Marsh Stream
STREAM RATING INFORMATION:
15. NC SAM Zone: r Mountains (M) {o Piedmont (P) r Inner Coastal Plain (I) r Outer Coastal Plain (0)
16. Estimated geomorphic l 1
valley shape (skip for r 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 mi`) ( Size 2 (0.1 to < 0.5 mi`) r Size 3 (0.5 to < 5 mi`) r Size 4 (>_ 5 mit)
for Tidal Marsh Stream)
ADDITIONAL INFORMATION:
18. Were regulatory considerations evaluated? {o Yes r No If Yes, check all that appy to the assessment area.
r Section 10 water r Classified Trout Waters r Water Supply Watershed ( r I r II r III r IV r V)
r Essential Fish Habitat r Primary Nursery Area r High Quality Waters/Outstanding Resource Waters
r Publicly owned property r NCDWR riparian buffer rule in effect r Nutrient Sensitive Waters
r Anadromous fish r 303(d) List r CAMA Area of Environmental Concern (AEC)
r Documented presence of a federal and/or state listed protected species within the assessment area.
List species:
r 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)
r A Water throughout assessment reach.
r B No flow, water in pools only.
{o C No water in assessment reach.
2. Evidence of Flow Restriction - assessment reach metric
r 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).
{o B NotA
3. Feature Pattern - assessment reach metric
r A A majority of the assessment reach has altered pattern (examples: straightening, modification above or below culvert).
{o B NotA.
4. Feature Longitudinal Profile - assessment reach metric
r 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).
{o B NotA
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).
r A < 10% of channel unstable
{o B 10 to 25% of channel unstable
r 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
r A r A Little or no evidence of conditions that adversely affect reference interaction
{o B (o B Moderate evidence of conditions (examples: berms, levees, down -cutting, aggradation, dredging) that adversely affect
reference interaction (examples: limited streamside area access, disruption offlood flows through streamside area,
leaky or intermittent bulkheads, causeways with floodplain constriction, minor ditching [including mosquito ditching])
r C r 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

Water Quality Stressors — assessment reach/intertidal zone metric
Check all that apply.
r A Discolored water in stream or intertidal zone (milky white, blue, unnatural water discoloration, oil sheen, stream foam)
F B Excessive sedimentation (burying of stream features or intertidal zone)
r C Noticeable evidence of pollutant discharges entering the assessment reach and causing a water quality problem
r D Odor (not including natural sulfide odors)
r E Current published or collected data indicating degraded water quality in the assessment reach. Cite source in the "Notes/Sketch"
section.
r F Livestock with access to stream or intertidal zone
r G Excessive algae in stream or intertidal zone
r H Degraded marsh vegetation in the intertidal zone (removal, burning, regular mowing, destruction, etc.)
r I Other: (explain in "Notes/Sketch" section)
r 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 streams, D2 drought or higher is considered a
drought.
r A Drought conditions and no rainfall or rainfall not exceeding 1 inch within the last 48 hours
r B Drought conditions and rainfall exceeding 1 inch within the last 48 hours
{o C No drought conditions
9 Large or Dangerous Stream — assessment reach metric
r Yes {o 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. {o Yes r 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)
r A Multiple aquatic macrophytes and aquatic mosses --F,E r F 5% oysters or other natural hard bottoms
(include liverworts, lichens, and algal mats) F m r G Submerged aquatic vegetation
a
r B Multiple sticks and/or leaf packs and/or emergent o � � r H Low -tide refugia (pools)
vegetation r 0 r I Sand bottom
r C Multiple snags and logs (including lap trees) L r J 5% vertical bank along the marsh
r D 5% undercut banks and/or root mats and/or roots O r K Little or no habitat
in banks extend to the normal wetted perimeter
r E Little or no habitat
*********************************REMAINING QUESTIONS ARE NOT APPLICABLE FOR TIDAL MARSH STREAMS**********************...
11. Bedform and Substrate —assessment reach metric (skip for Size 4 Coastal Plain streams and Tidal Marsh Streams)
Ila. r Yes {o No Is assessment reach in a natural sand -bed stream? (skip for Coastal Plain streams)
11b_ Bedform evaluated. Check the appropriate box(es).
r A Riffle -run section (evaluate 11c)
r B Pool -glide section (evaluate 11d)
r C Natural bedform absent (skip to Metric 12, Aquatic Life)
11 c. 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
{o r r r r Bedrock/sa pro lite
{o r r r r Boulder (256 — 4096 mm)
{o r r r r Cobble (64 — 256 mm)
r r r r r Gravel (2 — 64 mm)
r r r r {o Sand (.062 — 2 mm)
r r r r {o Silt/clay (< 0.062 mm)
{o r r r r Detritus
{o r r r r Artificial (rip -rap, concrete, etc.)
1ld. r Yes {o 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. r Yes {o 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. {o No Water r Other:
12b. r Yes r 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.
r rAdult frogs
r r Aquatic reptiles
r r Aquatic macrophytes and aquatic mosses (include liverworts, lichens, and algal mats)
r r Beetles (including water pennies)
r r Caddisf y larvae (Trichoptera [T])
r r Asian clam (Corbicula )
r r Crustacean (isopod/amphipod/crayfish/sh rim p)
r r Damselfly and dragonfly larvae
r r Dipterans (true flies)
r r Mayfly larvae (Ephemeroptera [E])
r r Megaloptera (alderfly, fshfly, dobsonfly larvae)
r r Midges/mosquito larvae
r r Mosquito fish (Gambusia) or mud minnows (Umbra pygmaea)

r r Mussels/Clams (not Corbicula )
r r Other fish
r r Salamanders/tadpoles
r r Snails
r r Stonefly larvae (Plecoptera [P])
r r Tipulid larvae
r r 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
r A r A Little or no alteration to water storage capacity over a majority of the streamside area
r B r B Moderate alteration to water storage capacity over a majority of the streamside area
r C r 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
r A r A Majority of streamside area with depressions able to pond water>_ 6 inches deep
r B r B Majority of streamside area with depressions able to pond water 3 to 6 inches deep
r C r 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 stream side area or within the
normal wetted perimeter of assessment reach.
LB RB
r Y r Y Are wetlands present in the streamside area?
r 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.
r A Streams and/or springs Qurisdictional discharges)
r B Ponds (include wet detention basins, do not include sediment basins or dry detention basins)
r C Obstruction that passes some flow during low -flow periods within assessment area (beaver dam, bottom -release dam)
r D Evidence of bank seepage or sweating (iron oxidizing bacteria in water indicates seepage)
r E Stream bed or bank soil reduced (dig through deposited sediment if present)
F F None of the above
17. Baseflow Detractors — assessment area metric (skip for Tidal Marsh Streams)
Check all that apply.
r A Evidence of substantial water withdrawals from the assessment reach (includes areas excavated for pump installation)
r B Obstruction not passing flow during low flow periods affecting the assessment reach (ex: watertight dam, sediment deposit)
r C Urban stream (>_ 24% impervious surface for watershed)
r D Evidence that the stream -side area has been modified resulting in accelerated drainage into the assessment reach
r E Assessment reach relocated to valley edge
r F None of the above
18. Shading — assessment reach metric (skip for Tidal Marsh Streams)
Consider aspect. Consider "leaf -on" condition.
{o A Stream shading is appropriate for stream category (may include gaps associated with natural processes)
r B Degraded (example: scattered trees)
r 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
{o A r A {o A r A > 100 -feet wide or extends to the edge of the watershed
r B r B r B r B From 50 to < 100 -feet wide
r C r C r C r C From 30 to < 50 -feet wide
r D r D r D r D From 10 to < 30 -feet wide
r E r E r E r 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
{o A {o A Mature forest
r B r B Non -mature woody vegetation or modified vegetation structure
r C r C Herbaceous vegetation with or without a strip of trees < 10 feet wide
r D r D Maintained shrubs
r E r 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: r
Abuts < 30 feet 30-50 feet
LB RB LB RB LB RB
r r r r r r Row crops
r B r B r B r B r B r B Maintained turf
r C r C r C r C r C r C Pasture (no livestock)/commercial horticulture
r D r D r D r D r D r 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
{o A {o A Medium to high stem density
r B r B Low stem density
r C r 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
{o A {o A The total length of buffer breaks is < 25 percent.
r B r B The total length of buffer breaks is between 25 and 50 percent.
r C r 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
{o A {o 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-
r B r 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.
r C r 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. r Yes {o No Was a conductivity measurement recorded?
If No, select one of the following reasons. {o No Water r Other:
25b. Check the box corresponding to the conductivity measurement (units of microsiemens per centimeter).
r A <46 r B 46 to < 67 r C 67 to < 79 r D 79 to < 230 r E >> 230
Notes/Sketch-
see Support Document

Draft NC SAM Stream Rating Sheet
Accompanies User Manual Version 1
Rating Calculator Version 1
Stream Site Name Publix Distribution Center
Stream Category Pb1
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)
Date of Evaluation 09/19/2019
Assessor Name/Organization E. Wright, H. Wines
YES
NO
vGc
intermittent
USACE/
NCDWR
Function Class Rating Summary
All Streams
Intermittent
(1) Hydrology
MEDIUM
MEDIUM
(2) Baseflow
HIGH
HIGH
(2) Flood Flow
MEDIUM
MEDIUM
(3) Streamside Area Attenuation
MEDIUM
MEDIUM
(4) Floodplain Access
MEDIUM
MEDIUM
(4) Wooded Riparian Buffer
HIGH
HIGH
(4) Microtopography
NA
NA
(3) Stream Stability
MEDIUM
MEDIUM
(4) Channel Stability
MEDIUM
MEDIUM
(4) Sediment Transport
LOW
LOW
(4) Stream Geomorphology
HIGH
HIGH
(2) Stream/Intertidal Zone Interaction
NA
NA
(2) Longitudinal Tidal Flow
NA
NA
(2) Tidal Marsh Stream Stability
NA
NA
(3) Tidal Marsh Channel Stability
NA
NA
(3) Tidal Marsh Stream Geomorphology
NA
NA
(1) Water Quality
HIGH
HIGH
(2) Baseflow
HIGH
HIGH
(2) Streamside Area Vegetation
HIGH
HIGH
(3) Upland Pollutant Filtration
HIGH
HIGH
(3) Thermoregulation
HIGH
HIGH
(2) Indicators of Stressors
NO
NO
(2) Aquatic Life Tolerance
OMITTED
NA
(2) Intertidal Zone Filtration
NA
NA
(1) Habitat
MEDIUM
MEDIUM
(2) In -stream Habitat
LOW
LOW
(3) Baseflow
HIGH
HIGH
(3) Substrate
LOW
LOW
(3) Stream Stability
MEDIUM
MEDIUM
(3) In -stream Habitat
LOW
LOW
(2) Stream -side Habitat
HIGH
HIGH
(3) Stream -side Habitat
HIGH
HIGH
(3) Thermoregulation
HIGH
HIGH
(2) Tidal Marsh In -stream Habitat
NA
NA
(3) Flow Restriction
NA
NA
(3) Tidal Marsh Stream Stability
NA
NA
(4) Tidal Marsh Channel Stability
NA
NA
(4) Tidal Marsh Stream Geomorphology
NA
NA
(3) Tidal Marsh In -stream Habitat
NA
NA
(2) Intertidal Zone Habitat
NA
NA
Overall
MEDIUM
MEDIUM

Accompanies User Manual Version 2
t:arcwator version z
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
Manual for detailed descriptions and explanations of requested information. Record in the "Notes/Sketch" section if any supplementary
measurements were performed. Seethe NC SAM User Manual for examples of additional measurements that maybe relevant.
NOTE EVIDENCE OF STRESSORS AFFECTING THE ASSESSMENT AREA (do not need to be within the assessment area).
PROJECT/ SITE INFORMATION:
1. Project name (if any): Public Distribution Center (S713-6) 2. Date of evaluation: 09/19/2019
3. Applicant/owner name: Public Super Markets Inc. 4. Assessor name/organization: E. Wright, H. Wines
5. County: Guilford 6. Nearest named water body
7. River Basin: Cape Fear on USGS 7.5 -minute quad: Little Alamance Creek
8. Site coordinates (decimal degrees, at lower end of assessment reach): 36.0823, -79.6574
STREAM INFORMATION: (depth and width can be approximations)
9. Site number (show on attached map): SAM-S7B-6 10. Length of assessment reach evaluated (feet): 437
11. Channel depth from bed (in riffle, if present) to top of bank (feet): 0.5 r Unable to assess channel depth.
12. Channel width at top of bank (feet): 2 13. Is assessment reach a swamp stream? r Yes r No
14. Feature type: r Perennial flow • Intermittent flow r Tidal Marsh Stream
STREAM RATING INFORMATION:
15. NC SAM Zone: r Mountains (M) {o Piedmont (P) r Inner Coastal Plain (I) r Outer Coastal Plain (0)
16. Estimated geomorphic l 1
valley shape (skip for r 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 mi`) ( Size 2 (0.1 to < 0.5 mi`) r Size 3 (0.5 to < 5 mi`) r Size 4 (>_ 5 mit)
for Tidal Marsh Stream)
ADDITIONAL INFORMATION:
18. Were regulatory considerations evaluated? {o Yes r No If Yes, check all that appy to the assessment area.
r Section 10 water r Classified Trout Waters r Water Supply Watershed ( r I r II r III r IV r V)
r Essential Fish Habitat r Primary Nursery Area r High Quality Waters/Outstanding Resource Waters
r Publicly owned property r NCDWR riparian buffer rule in effect r Nutrient Sensitive Waters
r Anadromous fish r 303(d) List r CAMA Area of Environmental Concern (AEC)
r Documented presence of a federal and/or state listed protected species within the assessment area.
List species:
r 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)
r A Water throughout assessment reach.
r B No flow, water in pools only.
{o C No water in assessment reach.
2. Evidence of Flow Restriction - assessment reach metric
{o 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 ora 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).
r B NotA
3. Feature Pattern - assessment reach metric
{o A A majority of the assessment reach has altered pattern (examples: straightening, modification above or below culvert).
r B NotA.
4. Feature Longitudinal Profile - assessment reach metric
r 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).
{o B NotA
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).
{o A < 10% of channel unstable
r B 10 to 25% of channel unstable
r 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
r A r A Little or no evidence of conditions that adversely affect reference interaction
{o B (o B Moderate evidence of conditions (examples: berms, levees, down -cutting, aggradation, dredging) that adversely affect
reference interaction (examples: limited streamside area access, disruption offlood flows through streamside area,
leaky or intermittent bulkheads, causeways with floodplain constriction, minor ditching [including mosquito ditching])
r C r 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

Water Quality Stressors — assessment reach/intertidal zone metric
Check all that apply.
r A Discolored water in stream or intertidal zone (milky white, blue, unnatural water discoloration, oil sheen, stream foam)
F B Excessive sedimentation (burying of stream features or intertidal zone)
r C Noticeable evidence of pollutant discharges entering the assessment reach and causing a water quality problem
r D Odor (not including natural sulfide odors)
r E Current published or collected data indicating degraded water quality in the assessment reach. Cite source in the "Notes/Sketch"
section.
r F Livestock with access to stream or intertidal zone
r G Excessive algae in stream or intertidal zone
r H Degraded marsh vegetation in the intertidal zone (removal, burning, regular mowing, destruction, etc.)
r I Other: (explain in "Notes/Sketch" section)
r 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 streams, D2 drought or higher is considered a
drought.
r A Drought conditions and no rainfall or rainfall not exceeding 1 inch within the last 48 hours
r B Drought conditions and rainfall exceeding 1 inch within the last 48 hours
{o C No drought conditions
9 Large or Dangerous Stream — assessment reach metric
r Yes {o 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. {o Yes r 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)
r A Multiple aquatic macrophytes and aquatic mosses --F,E r F 5% oysters or other natural hard bottoms
(include liverworts, lichens, and algal mats) F m r G Submerged aquatic vegetation
a
r B Multiple sticks and/or leaf packs and/or emergent o � � r H Low -tide refugia (pools)
vegetation r 0 r I Sand bottom
r C Multiple snags and logs (including lap trees) L r J 5% vertical bank along the marsh
r D 5% undercut banks and/or root mats and/or roots O r K Little or no habitat
in banks extend to the normal wetted perimeter
r E Little or no habitat
*********************************REMAINING QUESTIONS ARE NOT APPLICABLE FOR TIDAL MARSH STREAMS**********************...
11. Bedform and Substrate —assessment reach metric (skip for Size 4 Coastal Plain streams and Tidal Marsh Streams)
Ila. r Yes {o No Is assessment reach in a natural sand -bed stream? (skip for Coastal Plain streams)
11b_ Bedform evaluated. Check the appropriate box(es).
r A Riffle -run section (evaluate 11c)
r B Pool -glide section (evaluate 11d)
r C Natural bedform absent (skip to Metric 12, Aquatic Life)
11 c. 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
{o r r r r Bedrock/sa pro lite
{o r r r r Boulder (256 — 4096 mm)
{o r r r r Cobble (64 — 256 mm)
{o r r r r Gravel (2 — 64 mm)
r r r r r Sand (.062 — 2 mm)
r r r r r Silt/clay (< 0.062 mm)
{o r r r r Detritus
{o r r r r Artificial (rip -rap, concrete, etc.)
1ld. {o Yes r 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. r Yes {o 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. {o No Water r Other:
12b. r Yes r 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.
r rAdult frogs
r r Aquatic reptiles
r r Aquatic macrophytes and aquatic mosses (include liverworts, lichens, and algal mats)
r r Beetles (including water pennies)
r r Caddisf y larvae (Trichoptera [T])
r r Asian clam (Corbicula )
r r Crustacean (isopod/amphipod/crayfish/sh rim p)
r r Damselfly and dragonfly larvae
r r Dipterans (true flies)
r r Mayfly larvae (Ephemeroptera [E])
r r Megaloptera (alderfly, fshfly, dobsonfly larvae)
r r Midges/mosquito larvae
r r Mosquito fish (Gambusia) or mud minnows (Umbra pygmaea)

r r Mussels/Clams (not Corbicula )
r r Other fish
r r Salamanders/tadpoles
r r Snails
r r Stonefly larvae (Plecoptera [P])
r r Tipulid larvae
r r 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
r A r A Little or no alteration to water storage capacity over a majority of the streamside area
r B r B Moderate alteration to water storage capacity over a majority of the streamside area
r C r 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
r A r A Majority of streamside area with depressions able to pond water>_ 6 inches deep
r B r B Majority of streamside area with depressions able to pond water 3 to 6 inches deep
r C r 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
{o Y r Y Are wetlands present in the streamside area?
r r
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.
r A Streams and/or springs Qurisdictional discharges)
r B Ponds (include wet detention basins; do not include sediment basins or dry detention basins)
r C Obstruction that passes some flow during low -flow periods within assessment area (beaver dam, bottom -release dam)
F D Evidence of bank seepage or sweating (iron oxidizing bacteria in water indicates seepage)
r E Stream bed or bank soil reduced (dig through deposited sediment if present)
r F None of the above
17. Baseflow Detractors — assessment area metric (skip for Tidal Marsh Streams)
Check all that apply.
r A Evidence of substantial water withdrawals from the assessment reach (includes areas excavated for pump installation)
r B Obstruction not passing flow during low flow periods affecting the assessment reach (ex: watertight dam, sediment deposit)
r C Urban stream (>_ 24% impervious surface for watershed)
r D Evidence that the stream -side area has been modified resulting in accelerated drainage into the assessment reach
r E Assessment reach relocated to valley edge
r F None of the above
18. Shading — assessment reach metric (skip for Tidal Marsh Streams)
Consider aspect. Consider "leaf -on" condition.
{o A Stream shading is appropriate for stream category (may include gaps associated with natural processes)
r B Degraded (example: scattered trees)
r 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
{o A r A {o A r A > 100 -feet wide or extends to the edge of the watershed
r B r B r B r B From 50 to < 100 -feet wide
r C r C r C r C From 30 to < 50 -feet wide
r D r D r D r D From 10 to < 30 -feet wide
r E r E r E r 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
{o A {o A Mature forest
r B r B Non -mature woody vegetation or modified vegetation structure
r C r C Herbaceous vegetation with orwithout a strip of trees < 10 feet wide
r D r D Maintained shrubs
r E r 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: r
Abuts < 30 feet 30-50 feet
LB RB LB RB LB RB
r r r r r r Row crops
r B r B r B r B r B r B Maintained turf
r C r C r C r C r C r C Pasture (no livestock)/commercial horticulture
r D r D r D r D r D r 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
{o A {o A Medium to high stem density
r B r B Low stem density
r C r 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
{o A {o A The total length of buffer breaks is < 25 percent.
r B r B The total length of buffer breaks is between 25 and 50 percent.
r C r 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
r A r 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.
{t B {o 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.
r C r 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. r Yes {o No Was a conductivity measurement recorded?
If No, select one of the following reasons. {o No Water r Other:
25b. Check the box corresponding to the conductivity measurement (units of microsiemens per centimeter).
r A <46 r B 46 to < 67 r C 67 to < 79 r D 79 to < 230 r E >> 230
Notes/Sketch-
see Support Document

Draft NC SAM Stream Rating Sheet
Accompanies User Manual Version 1
Rating Calculator Version 1
Stream Site Name Publix Distribution Center (S713-6)
Stream Category Pb1
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)
Date of Evaluation 09/19/2019
Assessor Name/Organization E. Wright, H. Wines
YES
NO
vGc
intermittent
USACE/
NCDWR
Function Class Rating Summary
All Streams
Intermittent
(1) Hydrology
MEDIUM
MEDIUM
(2) Baseflow
MEDIUM
MEDIUM
(2) Flood Flow
MEDIUM
MEDIUM
(3) Streamside Area Attenuation
MEDIUM
MEDIUM
(4) Floodplain Access
MEDIUM
MEDIUM
(4) Wooded Riparian Buffer
HIGH
HIGH
(4) Microtopography
NA
NA
(3) Stream Stability
MEDIUM
MEDIUM
(4) Channel Stability
HIGH
HIGH
(4) Sediment Transport
LOW
LOW
(4) Stream Geomorphology
MEDIUM
MEDIUM
(2) Stream/Intertidal Zone Interaction
NA
NA
(2) Longitudinal Tidal Flow
NA
NA
(2) Tidal Marsh Stream Stability
NA
NA
(3) Tidal Marsh Channel Stability
NA
NA
(3) Tidal Marsh Stream Geomorphology
NA
NA
(1) Water Quality
HIGH
HIGH
(2) Baseflow
MEDIUM
MEDIUM
(2) Streamside Area Vegetation
HIGH
HIGH
(3) Upland Pollutant Filtration
HIGH
HIGH
(3) Thermoregulation
HIGH
HIGH
(2) Indicators of Stressors
NO
NO
(2) Aquatic Life Tolerance
OMITTED
NA
(2) Intertidal Zone Filtration
NA
NA
(1) Habitat
MEDIUM
MEDIUM
(2) In -stream Habitat
LOW
LOW
(3) Baseflow
MEDIUM
MEDIUM
(3) Substrate
LOW
LOW
(3) Stream Stability
HIGH
HIGH
(3) In -stream Habitat
LOW
LOW
(2) Stream -side Habitat
HIGH
HIGH
(3) Stream -side Habitat
HIGH
HIGH
(3) Thermoregulation
HIGH
HIGH
(2) Tidal Marsh In -stream Habitat
NA
NA
(3) Flow Restriction
NA
NA
(3) Tidal Marsh Stream Stability
NA
NA
(4) Tidal Marsh Channel Stability
NA
NA
(4) Tidal Marsh Stream Geomorphology
NA
NA
(3) Tidal Marsh In -stream Habitat
NA
NA
(2) Intertidal Zone Habitat
NA
NA
Overall
MEDIUM
MEDIUM

Accompanies User Manual Version 2
t:arcwator version z
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
Manual for detailed descriptions and explanations of requested information. Record in the "Notes/Sketch" section if any supplementary
measurements were performed. Seethe NC SAM User Manual for examples of additional measurements that maybe relevant.
NOTE EVIDENCE OF STRESSORS AFFECTING THE ASSESSMENT AREA (do not need to be within the assessment area).
PROJECT/ SITE INFORMATION:
1. Project name (if any): Public Distribution Center (S7C-7) 2. Date of evaluation: 09/19/2019
3. Applicant/owner name: Public Super Markets Inc. 4. Assessor name/organization: E. Wright, H. Wines
5. County: Guilford 6. Nearest named water body
7. River Basin: Cape Fear on USGS 7.5 -minute quad: Little Alamance Creek
8. Site coordinates (decimal degrees, at lower end of assessment reach): 36.0820, -79.6566
STREAM INFORMATION: (depth and width can be approximations)
9. Site number (show on attached map): SAM-S7C-7 10. Length of assessment reach evaluated (feet): 55
11. Channel depth from bed (in riffle, if present) to top of bank (feet): 4 r Unable to assess channel depth.
12. Channel width at top of bank (feet): 4 13. Is assessment reach a swamp stream? r Yes r No
14. Feature type: r Perennial flow • Intermittent flow r Tidal Marsh Stream
STREAM RATING INFORMATION:
15. NC SAM Zone: r Mountains (M) {o Piedmont (P) r Inner Coastal Plain (I) r Outer Coastal Plain (0)
16. Estimated geomorphic l 1
valley shape (skip for r 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 mi`) ( Size 2 (0.1 to < 0.5 mi`) r Size 3 (0.5 to < 5 mi`) r Size 4 (>_ 5 mit)
for Tidal Marsh Stream)
ADDITIONAL INFORMATION:
18. Were regulatory considerations evaluated? {o Yes r No If Yes, check all that appy to the assessment area.
r Section 10 water r Classified Trout Waters r Water Supply Watershed ( r I r II r III r IV r V)
r Essential Fish Habitat r Primary Nursery Area r High Quality Waters/Outstanding Resource Waters
r Publicly owned property r NCDWR riparian buffer rule in effect r Nutrient Sensitive Waters
r Anadromous fish r 303(d) List r CAMA Area of Environmental Concern (AEC)
r Documented presence of a federal and/or state listed protected species within the assessment area.
List species:
r 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)
r A Water throughout assessment reach.
r B No flow, water in pools only.
{o C No water in assessment reach.
2. Evidence of Flow Restriction - assessment reach metric
r 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).
{o B NotA
3. Feature Pattern - assessment reach metric
r A A majority of the assessment reach has altered pattern (examples: straightening, modification above or below culvert).
{o B NotA.
4. Feature Longitudinal Profile - assessment reach metric
{o 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).
r B NotA
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).
r A < 10% of channel unstable
r B 10 to 25% of channel unstable
{o 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
r A r A Little or no evidence of conditions that adversely affect reference interaction
r B r B Moderate evidence of conditions (examples: berms, levees, down -cutting, aggradation, dredging) that adversely affect
reference interaction (examples: limited streamside area access, disruption offlood flows through streamside area,
leaky or intermittent bulkheads, causeways with floodplain constriction, minor ditching [including mosquito ditching])
{o C (o 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

Water Quality Stressors — assessment reach/intertidal zone metric
Check all that apply.
r A Discolored water in stream or intertidal zone (milky white, blue, unnatural water discoloration, oil sheen, stream foam)
r B Excessive sedimentation (burying of stream features or intertidal zone)
r C Noticeable evidence of pollutant discharges entering the assessment reach and causing a water quality problem
r D Odor (not including natural sulfide odors)
r E Current published or collected data indicating degraded water quality in the assessment reach. Cite source in the "Notes/Sketch"
section.
r F Livestock with access to stream or intertidal zone
r G Excessive algae in stream or intertidal zone
r H Degraded marsh vegetation in the intertidal zone (removal, burning, regular mowing, destruction, etc.)
r I Other (explain in "Notes/Sketch" section)
F 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 or4 streams, D2 drought or higher is considered a
drought.
r A Drought conditions and no rainfall or rainfall not exceeding 1 inch within the last 48 hours
r B Drought conditions and rainfall exceeding 1 inch within the last 48 hours
fo C No drought conditions
9 Large or Dangerous Stream - assessment reach metric
r Yes fo 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. fo Yes r 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)
r A Multiple aquatic macrophytes and aquatic mosses --F,E r F 5% oysters or other natural hard bottoms
(include l verworts, lichens, and algal mats) F m r G Submerged aquatic vegetation
a
r B Multiple sticks and/or leaf packs and/or emergent o � � r H Low -tide refugia (pools)
vegetation r 0 r I Sand bottom
r C Multiple snags and logs (including lap trees) L r J 5% vertical bank along the marsh
r D 5% undercut banks and/or root mats and/or roots O r K Little or no habitat
in banks extend to the normal wetted perimeter
r E Little or no habitat
*********************************REMAINING QUESTIONS ARE NOT APPLICABLE FOR TIDAL MARSH STREAMS**********************...
11. Bedform and Substrate -assessment reach metric (skip for Size 4 Coastal Plain streams and Tidal Marsh Streams)
Ila. r Yes fo No Is assessment reach in a natural sand -bed stream? (skip for Coastal Plain streams)
11 b. Bedform evaluated. Check the appropriate box(es).
r A Riffle -run section (evaluate 11c)
r B Pool -glide section (evaluate 11d)
r C Natural bedform absent (skip to Metric 12, Aquatic Life)
11 c. 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
fo r r r r Bedrock/sa pro lite
fo r r r r Boulder (256 - 4096 mm)
f-' fo r r r Cobble (64 - 256 mm)
f-' fo r r r Gravel (2 - 64 mm)
f-' r r fo r Sand (.062 - 2 mm)
f-' r r fo r Silt/clay (< 0.062 mm)
fo r r r r Detritus
fo r r r r Artificial (rip -rap, concrete, etc.)
1ld. r Yes fo 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. r Yes fo 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. fo No Water r Other:
12b. r Yes r 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.
r rAdult frogs
r r Aquatic reptiles
r r Aquatic macrophytes and aquatic mosses (include liverworts, lichens, and algal mats)
r r Beetles (including water pennies)
r r Caddisfiy larvae (Trichoptera [T])
r r Asian clam (Corbicula )
r r Crustacean (isopod/amphipod/crayfish/sh rim p)
r r Damselfly and dragonfly larvae
r r Dipterans (true flies)
r r Mayfly larvae (Ephemeroptera [E])
r r Megaloptera (alderfly, fshfly, dobsonfly larvae)
r r Midges/mosquito larvae
r r Mosquito fish (Gambusia) or mud minnows (Umbra pygmaea)

r r Mussels/Clams (not Corbicula )
r r Other fish
r r Salamanders/tadpoles
r r Snails
r r Stonefly larvae (Plecoptera [P])
r r Tipulid larvae
r r 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
r A r A Little or no alteration to water storage capacity over a majority of the streamside area
r B r B Moderate alteration to water storage capacity over a majority of the streamside area
r C r 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
r A r A Majority of streamside area with depressions able to pond water>_ 6 inches deep
r B r B Majority of streamside area with depressions able to pond water 3 to 6 inches deep
r C r 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 stream side area or within the
normal wetted perimeter of assessment reach.
LB RB
r Y r Y Are wetlands present in the streamside area?
r 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.
r A Streams and/or springs (jurisdictional discharges)
r B Ponds (include wet detention basins; do not include sediment basins or dry detention basins)
r C Obstruction that passes some flow during low -flow periods within assessment area (beaver dam, bottom -release dam)
r D Evidence of bank seepage or sweating (iron oxidizing bacteria in water indicates seepage)
F E Stream bed or bank soil reduced (dig through deposited sediment if present)
r F None of the above
17. Baseflow Detractors — assessment area metric (skip for Tidal Marsh Streams)
Check all that apply.
r A Evidence of substantial water withdrawals from the assessment reach (includes areas excavated for pump installation)
r B Obstruction not passing flow during low flow periods affecting the assessment reach (ex: watertight dam, sediment deposit)
r C Urban stream (>_ 24% impervious surface for watershed)
r D Evidence that the stream -side area has been modified resulting in accelerated drainage into the assessment reach
r E Assessment reach relocated to valley edge
r F None of the above
18. Shading — assessment reach metric (skip for Tidal Marsh Streams)
Consider aspect. Consider "leaf -on" condition.
{o A Stream shading is appropriate for stream category (may include gaps associated with natural processes)
r B Degraded (example: scattered trees)
r 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
{o A r A {o A r A > 100 -feet wide or extends to the edge of the watershed
r B r B r B r B From 50 to < 100 -feet wide
r C r C r C r C From 30 to < 50 -feet wide
r D r D r D r D From 10 to < 30 -feet wide
r E r E r E r 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
{o A {o A Mature forest
r B r B Non -mature woody vegetation or modified vegetation structure
r C r C Herbaceous vegetation with or without a strip of trees < 10 feet wide
r D r D Maintained shrubs
r E r 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: r
Abuts < 30 feet 30-50 feet
LB RB LB RB LB RB
r r r r r r Row crops
r B r B r B r B r B r B Maintained turf
r C r C r C r C r C r C Pasture (no livestock)/commercial horticulture
r D r D r D r D r D r 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
{o A {o A Medium to high stem density
r B r B Low stem density
r C r 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
{o A {o A The total length of buffer breaks is < 25 percent.
r B r B The total length of buffer breaks is between 25 and 50 percent.
r C r 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
r A r 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.
{t B {o 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.
r C r 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. r Yes {o No Was a conductivity measurement recorded?
If No, select one of the following reasons. {o No Water r Other:
25b. Check the box corresponding to the conductivity measurement (units of microsiemens per centimeter).
r A <46 r B 46 to < 67 r C 67 to < 79 r D 79 to < 230 r E >> 230
Notes/Sketch-
see Support Document

Draft NC SAM Stream Rating Sheet
Accompanies User Manual Version 1
Rating Calculator Version 1
Stream Site Name Publix Distribution Center (S7C-7)
Stream Category Pb1
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)
Date of Evaluation 09/19/2019
Assessor Name/Organization E. Wright, H. Wines
YES
NO
vGc
intermittent
USACE/
NCDWR
Function Class Rating Summary
All Streams
Intermittent
(1) Hydrology
LOW
LOW
(2) Baseflow
HIGH
HIGH
(2) Flood Flow
LOW
LOW
(3) Streamside Area Attenuation
LOW
LOW
(4) Floodplain Access
LOW
LOW
(4) Wooded Riparian Buffer
HIGH
HIGH
(4) Microtopography
NA
NA
(3) Stream Stability
LOW
LOW
(4) Channel Stability
LOW
LOW
(4) Sediment Transport
LOW
LOW
(4) Stream Geomorphology
MEDIUM
MEDIUM
(2) Stream/Intertidal Zone Interaction
NA
NA
(2) Longitudinal Tidal Flow
NA
NA
(2) Tidal Marsh Stream Stability
NA
NA
(3) Tidal Marsh Channel Stability
NA
NA
(3) Tidal Marsh Stream Geomorphology
NA
NA
(1) Water Quality
HIGH
HIGH
(2) Baseflow
HIGH
HIGH
(2) Streamside Area Vegetation
HIGH
HIGH
(3) Upland Pollutant Filtration
HIGH
HIGH
(3) Thermoregulation
HIGH
HIGH
(2) Indicators of Stressors
NO
NO
(2) Aquatic Life Tolerance
OMITTED
NA
(2) Intertidal Zone Filtration
NA
NA
(1) Habitat
MEDIUM
MEDIUM
(2) In -stream Habitat
LOW
LOW
(3) Baseflow
HIGH
HIGH
(3) Substrate
LOW
LOW
(3) Stream Stability
LOW
LOW
(3) In -stream Habitat
LOW
LOW
(2) Stream -side Habitat
HIGH
HIGH
(3) Stream -side Habitat
MEDIUM
MEDIUM
(3) Thermoregulation
HIGH
HIGH
(2) Tidal Marsh In -stream Habitat
NA
NA
(3) Flow Restriction
NA
NA
(3) Tidal Marsh Stream Stability
NA
NA
(4) Tidal Marsh Channel Stability
NA
NA
(4) Tidal Marsh Stream Geomorphology
NA
NA
(3) Tidal Marsh In -stream Habitat
NA
NA
(2) Intertidal Zone Habitat
NA
NA
Overall
MEDIUM
MEDIUM

Attachment 3:
NC SAM Photo Document

r10so
• •
TIMMONS GROUP
YOUR VISION ACHIEVED THROUGH OURS.
Publix Distribution Center
NC SAM Evaluation
09/18/2019
Photo 2: SAM -S5-1. Downstream view of Impact S5. (09/18/2019, E. Wright)

• r •
TIMMONS GROUP
YOUR VISION ACHIEVED THROUGH OURS.
Publix Distribution Center
NC SAM Evaluation
09/18/2019
Photo 4: SAM -S4-2. Downstream view of Impact S4. Water in pools only. (09/18/2019, E. Wright)

i. t 3 •i. i l\, 4 t, iyP s. +� d.FYI /
.w+y -•` - _ � � A SWI- 'ti i' i. ��- a ! - - - i- .
IL
MOW
ilk
16
Ab
40

\ ► T "
rta '
_ 9"1$:2'019 �'•�.

• r •
TIMMONS GROUP
YOUR VISION ACHIEVED THROUGH OURS.
Publix Distribution Center
NC SAM Evaluation
09/18/2019
Photo 9: SAM -S3-3. View of channel degradation and debris. Riparian area on left bank is in view.
Photo 10: SAM -S8-4. Downstream view of Impact S8. (09/18/2019, E. Wright)

• r •
TIMMONS GROUP
YOUR VISION ACHIEVED THROUGH OURS.
Publix Distribution Center
NC SAM Evaluation
09/18/2019
Photo 12: SAM -S8-4. Downstream view of Impact S8 and riparian area. (09/18/2019, E. Wright)

• r •
TIMMONS GROUP
YOUR VISION ACHIEVED THROUGH OURS.
Photo
,17: SAM-SXView of channel at Im
�ir ,.. _ ".ti U.1k,1f
Publix Distribution Center
NC SAM Evaluation
09/18/2019
Photo 18: SAM-SX7. Top of Impact SX. (09/18/2019, E. Wright)

• r •
TIMMONS GROUP
YOUR VISION ACHIEVED THROUGH OURS.
Publix Distribution Center
NC SAM Evaluation
09/18/2019
Photo 20: SAM -S713-6. View from downstream section of assessment reach for Impact S713. Break in
assessment reach is at existing road crossing shown here. (09/18/2019, E. Wright)

• r •
TIMMONS GROUP
YOUR VISION ACHIEVED THROUGH OURS.
Publix Distribution Center
NC SAM Evaluation
09/18/2019
Photo 21: SAM -S713-6. View of evaluated portion of Impact S713. (09/18/2019, E. Wright)

Attachment 4:
Proposed Mitigation

Impacts Table
Impact ID
Temporary
Impact
Permanent
(Open
Water)
Wetland (sq. ft)
Conversion
Permanent Temporary Permanent
Stream Buffers (sq. ft)
Impact
Temporary Permanent
Stream (If)
Impact
Temporary Permanent
Resource
Type
Mitigation
Ratio
Stream
Mitigation
Required
Wetland
Mitigation
Required
Buffer
Mitigation
Required
Confirmed
Delineation
Resource ID
W1
142
PFO
2:1
-
284
-
W33
W2
743
PFO
2:1
-
1,486
-
W29
W2.2"
21
PFO
2:1
-
42
-
W29
V\/3 -A
87
PFO
2:1
-
174
-
W29
V\/3 -B
5,035
PFO
2:1
-
10,070
-
W30
V\/3 -C
1,081
PFO
2:1
-
2,162
-
W31
W4
1,468
PFO
2:1
-
2,936
-
W34
W5 -A
64,480
POW
NR
-
-
-
Pond 1
W5 -B
2,483
PEM
2:1
-
4,966
-
W38
W6
2,281
PFO
2:1
-
4,562
-
W35
W7
9,160
POW
NR
-
-
-
Pond 2
W8
255
PFO
2:1
-
510
-
W36
W9
976
PFO
2:1
-
1,952
-
W37
W10
285
PFO
2:1
-
570
-
W17
W10.2"
85
PFO
2:1
-
170
-
W17
W11
519
PFO
2:1
-
1,038
-
W4
W12 -A
810
PFO
2:1
-
1,620
-
V\/3A
W12 -B
472
PFO
2:1
-
944
-
V\/3B
W13
5,896
PFO
2:1
-
11,792
-
W2
W14
7,167
PFO
2:1
-
14,334
-
W1
W15
132
PFO
2:1
-
264
-
W8
W16
67
PFO
2:1
-
134
-
W9
W17
87
PFO
2:1
-
174
-
W23
W18 -A
422
PFO
2:1
-
844
-
W10A
W18 -B
376
PFO
2:1
-
752
-
W10B
W1 8-C
191
PFO
2:1
-
382
-
W11
W18 -D
822
PFO
2:1
-
1,644
-
W12
W18 -E
1,543
PFO
2:1
-
3,086
-
W13
W19
4,935
PFO
2:1
-
9,870
-
W6
W19.2"
3,461
PFO
2:1
-
6,922
-
W6
S 1-A
290
R3
2:1
580
-
-
K
S1 -B
687
R4
2:1
1,374
-
-
K
S1 -C
28
R4
2:1
56
-
-
O
S2
318
R4
1.5:1
477
-
-
L
S3
204
R3
1:1
204
-
-
S1
S3.2"
31
R3
1.5:1
47
-
-
S1
S4
283
R4
1.5:1
425
-
-
S1
S5
57
R4
1:1
57
-
-
S1
S6
373
R4
2:1
746
-
-
H
S7 -A
1,479
R3
2:1
2,958
-
-
F
S7 -B
707
R4
1.5:1
1,061
-
-
F
S7 -C
55
R4
1.5:1
83
-
-
G
S8
10
R3
NR
-
-
-
J
S9
10
R3
NR
-
-
-
A
B3 -Z1
54,295
Zone 1
3:1
-
-
162,885
-
B3 -Z2
40,628
Zone 2
1.5:1
-
-
60,942
-
B4 -Z2
1,880
Zone 2
NR
-
-
-
-
B6 -Z1
675
Zone 1
NR
-
-
-
-
B6 -Z2
245
Zone 2
NR
-
-
-
-
B7 -Z1
607
Zone 1
NR
-
-
-
-
B7 -Z2
405
Zone 2
NR
- I
-
-
-
Total 0 sq ft
0.0 ac
73,640 sq ft 41,842 sq ft 0 sq ft 0 sq ft
1.7 ac 1.0 ac 0.0 ac 0.0 ac
1,932 sq ft
0.04 ac
96,803 sq ft
2.2 ac
20 If 4,512 If
-
-
8,066 If
1.92 ac
223,827 sq ft
5.14 ac
-
NR = Not Required for Mitigation
"Secondary impact