HomeMy WebLinkAbout20191146 Ver 1_20190626 RPT WOTUS DRAFT V2 with attachments_20190826
Waters of the United States Technical Report
The Chemours Company
Fayetteville Works Project
Old Outfall 002
Bladen County, North Carolina
Prepared by:
Parsons
June 2019
Table of Contents
i
Table of Contents
0BINTRODUCTION ....................................................................................................................... 1
Introduction ...................................................................................................................................................... 1
Project Location and Background .................................................................................................................. 1
1BMETHODOLOGY ...................................................................................................................... 3
Desktop Review ............................................................................................................................................... 3
NWI and Floodplain Mapping ........................................................................................................ 3
USGS Mapping .................................................................................................................................. 3
NRCS Soil Mapping .......................................................................................................................... 3
Watersheds........................................................................................................................................................ 3
Field Reconnaissance ....................................................................................................................................... 4
2BRESULTS ...................................................................................................................................... 5
Wetlands............................................................................................................................................................ 5
Wetland 1 ............................................................................................................................................ 5
Wetlands 2 .......................................................................................................................................... 5
Streams .............................................................................................................................................................. 5
2BCONCLUSION ............................................................................................................................ 7
3BREFERENCES .............................................................................................................................. 8
4BLIST OF ACRONYMS ............................................................................................................... 9
APPENDIX A –MAPPING
Project Area Vicinity Map – Old Outfall 002
Project Feature Map
NWI Map
USGS 7.5-Minute Topographic Map – Duart Quadrangle
USGS 7.5-Minute Topographic Map (Excerpt)
FEMA Map
NRCS Soil Map
APPENDIX B – PROJECT AREA PHOTOGRAPHS
APPENDIX C – WETLAND DETERMINATION DATA FORMS
APPENDIX D – STREAM DATA FORMS
Introduction
1
1 0BIntroduction
Introduction
This Waters for the United States (WOTUS) report presents the results of a field survey conducted on behalf
of The Chemours Company. On February 27, 2019, a field survey was conducted by Parsons to determine
the location and extent of any potential WOTUS, including wetlands and waterbodies, that would be
regulated by the Clean Water Act (CWA) and/or Section 10 of the Rivers and Harbors Act (RHA) subject
to the jurisdiction of the United States Army Corps of Engineers (USACE) and the United States
Environmental Protection Agency (USEPA). The field survey was also conducted to determine the location
and extent of any potential Waters of the State which include any wetland, stream, or waterbody as defined
in North Carolina’s General Statute 143-212.
Project Location and Background
On July 1, 2015, The Chemours Company, a spin-off company from DuPont, became the owner of the 2,177-
acre property along with DuPont’s manufacturing units. The Chemours Company continues to use the
property as a manufacturing facility (Fayetteville Works) of plastic sheeting, fluorochemicals, and
intermediates for plastic manufacturing.
The Chemours Company Fayetteville Works Project area is located approximately 15 miles southeast of
the City of Fayetteville in Bladen County, North Carolina. The 2,177-acre site is relatively flat and has
undeveloped, open land and woodland. It is bounded on the east by the Cape Fear River and on the west
by North Carolina Highwater 87, and on the north and south by farmland.
On February 25, 2019, the North Carolina Superior Court for Bladen County entered a Consent Order (CO)
among The Chemours Company FC, LLC (Chemours) and the State of NC and Cape Fear River Watch to
address discharges of perfluoroalkyl and polyfluoroalkyl substances (PFAS) at the Chemours Fayetteville
Works (the Site). Among other things, the CO requires Chemours to develop a remedial plan for reducing
PFAS loading from Old Outfall 002 at the Site to the Cape Fear River . Design and implementation details
for near-term remedial actions at the facility have been developed 1 (Parsons 2018). Ongoing planning
documents addressed PFAS releases to groundwater from historical and current operations. An option
considered in these documents included the capture and pumping of groundwater to a new wastewater
treatment facility designed to treat PFAS. Two pump station locations were considered; however, the study
area discussed below is the only pump station location currently being considered. According to the CO,
by September 30, 2020, Chemours shall implement such measures to reduce PFAS loading from Old Outfall
002 to the Cape Fear River that will achieve results that are 99% effective in controlling indicator parameters
[GenX and PFMOAA]. To meet this PFAS reduction, Chemours will construct an instream structure in Old
1 Per a Consent Order, dated February 25, 2019, The Chemours Company denies any violation of any law,
regulation or permit, and has agreed remediation to avoid the expense, burden, and uncertainty of
litigation and to address community concerns about the facility.
Introduction
2
Outfall 002 stream and a water treatment facility. The instream structure would create a small
impoundment and the water in this impoundment would be pumped to the new treatment facility.
The study area is located west of Glengerry Road, spanning across an unnamed tributary (UNT) to the
Cape Fear River. An outfall (Old Outfall 002) is located along the tributary that eventually passes under
Glengerry Road. Detailed mapping of the project area is provided in Appendix A. On February 27, 2019, a
field survey was conducted by Parsons to determine the location and extent of any potential WOTUS within
the study area for the proposed capture and treatment facility. This report presents the results of that field
survey.
Methodology
3
2 1BMethodology
Desktop Review
Prior to field investigations, a desktop analysis of available information was reviewed, and potential
wetland areas were identified using published data, including: National Wetlands Inventory (NWI) maps;
United States Geological Survey (USGS) 7.5-minute series topographic maps; and Natural Resources
Conservation Service (NRCS) soil mapping for Bladen County, North Carolina.
NWI and Floodplain Mapping
The NWI mapping was used as an initial screen to determine locations of potential water resources within
the project area. NWI wetlands are illustrated in the detailed mapping provided in Appendix A. Wetlands
on NWI maps are classified in accordance with (Cowardin et al. 1979).
USGS Mapping
During review of USGS 7.5-minute series topo mapping (Appendix A), one intermittent (dashed blue line)
stream (Old Outfall 002 stream) was noted within the project area. This intermittent stream is an unnamed
tributary to the Cape Fear River. The upstream drainage of this tributary is 0.7 square miles (USGS 2019).
The western boundary of the study area is approximately 1,200 feet west of the Cape Fear River. The Cape
Fear River is a 202-mile long river that touches parts of Harnett, Cumberland, Bladen, Columbus, Pender,
Brunswick, and New Hanover counties in North Carolina before emptying into the Atlantic Ocean.
NRCS Soil Mapping
NRCS database includes a listing of soil map units that relate to specific soil series. A soil series is the
lowest, most homogeneous class in the soil taxonomy system. Each soil series has distinct soil attributes
that are defined by the NRCS. The soil attributes include physical and chemical properties and interpretive
groupings produced by the NRCS, including attributes that relate to potential soil impacts. Examples of
those soil attributes include the topographic setting and average slope, hydric soil conditions, drainage
characteristics, susceptibility to water and wind erosion, and suitability for use as farmland. The NRCS
classifies each soil type as follows: hydric (100%), predominately hydric (66-99%), partially hydric (33-65%),
predominately non-hydric (1-32%), and not-hydric (0%).
Hydric soils are soils that are inundated with water long enough to produce anaerobic conditions, and they
are an indicator of jurisdictional wetlands. Generally, hydric soils are those soils that are poorly drained or
very poorly drained. Hydric soils may indicate the presence of wetlands or high-water tables.
According to the Soil Survey Geographic Database, two mapped soil units fall within the study area of The
Chemours Company Fayetteville Works Project: Dystrochepts, steep (non-hydric) (79.4%) and Wagram
fine sand, 0 to 6 percent slopes (predominantly non-hydric) (20.6%). NRCS soil map units are illustrated in
the detailed mapping provided in Appendix A.
Watersheds
The Chemours Company Fayetteville Works Project is located within the following hydrologic unit code
(HUC) 12-digit watersheds: Phillips Creek-Cape Fear River (030300050104). The Phillips Creek-Cape Fear
River watershed has an area of 44.0 square miles (NCWSN 2019). Landcover types within this watershed
Methodology
4
include wetlands (33.0%), agriculture (19.1%), shrubland (16.7%), grassland (2.1%), forest (24.4%),
developed (2.9%), and open water (1.8%) (NCWSN 2019).
Field Reconnaissance
A field survey was conducted on February 27, 2019 to determine the presence of streams, wetlands, and
other water resources within the project area (i.e., the proposed capture and treatment area). Wetlands,
streams, and other waters were evaluated in the field and mapped with a handheld Global Positioning
System (GPS) unit (Trimble Geo7x). Data were recorded on applicable datasheets and features were
photographed. The GPS data was converted to ArcGIS shapefiles, data was attributed, and entered into the
project GIS database.
Wetlands were delineated using guidance set forth in the 1987 Corps of Engineers Wetlands Delineation
Manual (USACE 1987) and the Regional Supplement to the Corps of Engineers Wetland Delineation Manual:
Atlantic and Gulf Coastal Plain Region (Version 2.0) (USACE 2010). Data points were taken in locations that
exhibited one (or more) wetland indicators based on visual observations and for upland locations adjacent
to the wetlands. If all indicators were missing, no formal data was collected.
Streams were evaluated using the 2010 North Carolina Division of Water Quality (NCDWQ) Methodology
for Identification of Intermittent and Perennial Streams and Their Origins (NCDWQ 2010). The upstream
drainage area for each stream was calculated using StreamStats Version 4.3 (USGS 2019). All streams were
photographed and mapped with a GPS unit.
Results
5
3 2BResults
Wetlands
The field investigation resulted in the identification of two (2), likely jurisdictional, wetlands in the vicinity
of the project area, totally 0.05 acre. Detailed mapping of these features is provided in Appendix A. Project
area photographs are presented in Appendix B. The wetland determination data forms and accompanying
upland data forms, as well as, wetland functions and values datasheets are presented in Appendix C.
Wetland 1
Wetland 1 is a small, 0.01-acre groundwater-fed seep within a bottomland hardwood forest, south of Old
Outfall 002. The small seep receives stormwater runoff and has groundwater to the surface. The depressi on
appears to remain saturated for long durations during the growing season. Dominant vegetation within
this wetland includes loblolly pine (Pinus taeda), American holly (Ilex opaca), and red maple (Acer rubrum).
Within the wetland, soils are silt loam that transition to sandy loam at a depth of two inches. A lot of organic
matter is present in the top two inches of soil. Below two inches, the soil becomes saturated. At a depth of
eight inches, the soils become a slurry. A strong hydrogen sulfide odor was o bserved. Wetland hydrology
indicators include saturation, a high-water table, water-stained leaves, and a hydrogen sulfide odor.
The upland data point (Upland 1) is well drained. The upland is dominated by silver maple (Acer
saccharinum), American beech (Fagus grandifolia), and American holly (Ilex opaca). Soils are a sandy loam.
Fairly well drained on a slope above Wetland 1.
Wetlands 2
Wetland 2 is a small, 0.04-acre road ditch wetland along Glengerry Road. Dominant vegetation within this
wetland includes common rush (Juncus effuses). Soils are a sandy loam that are saturated to the surface. The
area receives surface water runoff during stormwater events and appears to receive intermittent
groundwater seepage from the uplands to the west. Soils were inundated up to two inches in some portions
of the wetland. Filamentous algae was observed in inundated portions of the wetland.
Streams
Field investigation resulted in the identification of two, likely jurisdictional, streams within the project area,
totaling approximately 300 linear feet.
UNT-1 to Cape Fear River (Old Outfall 002)
UNT-1 to Cape Fear River is a deeply incised stream bed below Old Outfall 002 of the Fayetteville Works
site. Most of the base flow within this stream is from groundwater. At the time of the field survey, a portion
of the area was flooded with backwater from the Cape Fear River. UNT-1 to Cape Fear River is shown as
an intermittent stream on USGS 7.5-minute series topographic mapping; however, based on the 2010 North
Carolina Division of Water Quality Methodology for Identification of Intermittent and Perennial Streams and Their
Origins, this is a perennial stream. This determination was supported by a NCDWQ Stream Identification
Results
6
Form score of 44.25 2 . The upstream drainage of this tributary is 0.7 square miles (USGS 2019).
Approximately 300 linear feet of UNT-1 to Cape Fear River lies within the study area, of which,
approximately 70 linear feet, is encapsulated in a culvert. UNT-1 to Cape Fear River is likely a WOTUS
because of the presence of an OHWM and its connectivity to the Cape Fear River, a traditionally navigable
waterway.
UNT-2 to Cape Fear River
UNT-2 to Cape Fear River is an ephemeral channel that enters UNT -1 to Caper Fear River just west of the
study area. UNT-2 to Cape Fear River is not shows on USGS 7.5-minute series topographic mapping;
however, based on the 2010 North Carolina Division of Water Quality Methodology for Identification of
Intermittent and Perennial Streams and Their Origins, this is an ephemeral stream. This determination was
supported by a NCDWQ Stream Identification Form score of 11.75. UNT-2 to Cape Fear River lies outside
of the study area. UNT-2 to Cape Fear River is likely a WOTUS because of the presence of an OHWM
(observed outside of the study area) and its connectivity via UNT-1 to the Cape Fear River, a traditionally
navigable waterway.
UNT-3 to Cape Fear River
UNT-3 to Cape Fear River is an ephemeral channel (primarily a road ditch) parallel to Glengerry Road.
UNT-3 to Cape Fear River is not shown on USGS 7.5-minute series topographic mapping; however, based
on the 2010 North Carolina Division of Water Quality Methodology for Identification of Intermittent and Perennial
Streams and Their Origins, this is an ephemeral stream. This determination was supported by a NCDWQ
Stream Identification Form score of 12.25. Approximately 15 linear feet of UNT-3 to Cape Fear River lies
within the study area, all off which is currently encapsulated within a culvert. UNT-3 to Cape Fear River is
likely a WOTUS because of the presence of an OHWM (observed outside of the study area) and its
connectivity via UNT-1 to the Cape Fear River, a traditionally navigable waterway.
2 Per the 2010 North Carolina Division of Water Quality Methodology for Identification of Intermittent and
Perennial Streams and Their Origins, a stream is ephemeral if it obtains a score less than 19. A stream is at
least intermittent if it obtains a score greater than or equal to 19. A stream is perennial is it obtains a score
greater than or equal to 30.
Conclusion
7
4 2BConclusion
Based on the field review, the project area has features that are likely WOTUS. Two (2) streams, totaling
315 linear feet, were identified within the project area. One additional stream was identified adjacent to the
project area. Two (2) wetlands, totaling 0.05 acre, were identified in the vicinity of the project area.
Efforts to avoid, minimize, and mitigate impacts to WOTUS will continue through the design phase of the
project. If impacts are unavoidable, mitigation may be required. The final determination of jurisdictional
waters is ultimately made by the USACE. This report reflects the analysis and best judgment of the wetland
scientists based on the guidelines set forth by the USACE.
References
8
4 3BReferences
The list of published references and information sources is presented below.
Cowardin et al.
1979 Cowardin, L.M., Carter, V., Golet, F.C., and LaRoe, E.T. Classification of Wetlands and
Deepwater Habitats of the United States. FWS/OBS-79/31, U.S. Fish and Wildlife Service, Office of
Biological Services, Washington, DC, December 1979.
North Carolina Division of Water Quality
2010 Methodology for Identification of Intermittent and Perennial Streams and Their Origins. Version
4.11. [http://portal.ncdenr.org/c/document_library/get_file?uuid=0ddc6ea1 -d736-4b55-8e50-
169a4476de96&groupId=38364]
North Carolina Watershed Stewardship Network (NCWSN)
2019 Watershed Stewardship Network. Phillips Creek-Cape Fear River. 2019.
[http://wsnet.renci.org/htmlNew/huc_report/index.html?huc=030300050104 ]
Natural Resources Conservation Service (NRCS)
2019 Natural Resources Conservation Service, United States Department of Agriculture. Web Soil
Survey. [https://websoilsurvey.sc.egov.usda.gov/App/HomePage.htm]
Parsons
2018 Focused Remedial Action Plan for PFAS in Groundwater. Chemours Fayetteville Works. RCRA
Permit No. NCD047368642-R2-M3. March 2018.
U.S. Army Corps of Engineers (USACE)
1987 Wetlands Research Program Technical Report Y-87-1 (online edition), Corps of Engineers, 1987
Wetlands Delineation Manual. [http://www.cpe.rutgers.edu/Wetlands/1987-Army-Corps-
Wetlands-Delineation-Manual.pdf]
2010 Regional Supplement to the Corps of Engineers Wetland Delineation Manual: Atlantic and Gulf
Coastal Plain Region (Version 2.0), November 2010.
[https://usace.contentdm.oclc.org/utils/getfile/collection/p266001coll1/id/7594 ]
U.S. Geological Survey (USGS)
2019 Stream Stats. Version 4.3. [https://streamstats.usgs.gov/ss/]
List of Acronyms
9
5 4BList of Acronyms
The list of acronyms is shown in the table below.
Acronym Full Acronym Reference
CWA Clean Water Act
GenX hexafluoropropylene oxide dimer acid (HFPO-DA)
GIS geographic information system
GPS global positioning system
HUC hydrologic unit code
NCDWQ North Carolina Division of Water Quality
NRCS Natural Resources Conservation Service
NWI National Wetlands Inventory
PFAS Perfluoroalkyl and polyfluoroalkyl substance
PFMOAA 2,2-difluoro-2(trifluoromethoxy)acetic acid
RAOs Remedial Action Objectives
RAP Remedial Action Plan
RHA River and Harbors Act
US United States
USACE United States Army Corps of Engineers
USEPA United States Environmental Protection Agency
USGS United States Geological Survey
WOTUS Waters of the United States
Appendix A
A Mapping
P r o j e c t
Project Area Vicinity Map – Old Outfall 002
Project Feature Map
NWI Map
USGS 7.5-Minute Topographic Map – Duart Quadrangle
USGS 7.5-Minute Topographic Map (Excerpt)
FEMA Map
NRCS Soil Map
Appendix A
Appendix A
Results
[
The Chemour CompanyFayetteville WorksCumberland County, N orth Carolina
0 1,250 2,500625Feet
W illis Creek
Swans Creek
Unnamed Tributary toWillis Creek
K i r k s Mill Creek
GeorgiaBranch
OldOut fa l l #2
MinesCre e k
Unnamed Tributary to the Cape Fear River
Georgia Branch CapeFearRiverWi
llis
Creek
Perennial Stream
Appendix A
Appendix A
USGS 7.5 Minute Topographic Map (Excerpt) – Duart Quadrangle
Old Outfall 002
Appendix A
FEMA Floodplain Information
Results
Map Unit Legend
MAP LEGEND
Armor Interest (A01)
Map Unit Symbol Map Unit Name
Acres In AOI
Percent of A01
0YF Dystrochrepts, steep
2.5
79.4%
WaB Wag ram fne sand, 0 to 6
permnt slopes
0.6
20.6°
Totals for Area of Interest
3.1
100.0'%
MAP LEGEND
Armor Interest (A01)
Area of Interest W1)
Suits
O
Sail MnpUnit Porygahs
,"•
Sail Map Unit Lines
0
Sail Map Unit Ports
Special
Paint Features
n
Bigv Oul
Borrow Pik
Clay Spat
Closed Depression
Gravel PR
Gravelly Spat
Landllll
A.
Lava Flow
Marsh cr swamp
Mina or Quarry
0
Miscellaneous Water
Perennial Water
Rock Outtrop
+
So HMO Spot
. :
Sandy Opot
4W
Severely Eroded Spot
Sinkhole
Slide or Slip
Sadie Spot
tg SpdIArea
G Stony Spat
Very Stang Spot
uuet Spat
Other
Special Line Feat.tas
Water Features
Streams and Canals
Transpartati on
i -i-+ Rs IN
n+ Inlerstita Highways
US Routes
Major Roads
Local Roads
6dcKgrountl
W6 AerialPhatography
MAP INFORMATION
The soil surveys that comprise your AOl •mere mapped at
1:24.600_
Warning: Soil Map may net bevaIid atINs scale.
Enlargement of maps beycnd the stele of mapping can cause
misunderstanding of the detail of mapping and accuracy of sail
line placement. The maps do not show the small areas of
contrasting sails that could have been shown at a mars deialled
scale.
Ptease rely on the bar scale on each map sheet for map
mea surements.
Soume of Map: Ne ural Resouroes Con servallon Serviat~
Web Sail Survey URL:
Cacrdinot eSystLm: WebMercator tEPSG:3857j
Map s from the Web Soil Survey are based on the Web Mercator
projection; which preserves directicn and shape but distorts
distanoe and area. A projection that oreso"s area, suoh as the
Albers equal-area conicprejection, should he used if more
accurate calculations of distance or area are required.
This product isgeneratedfrom the USDA-NRCS certified data as
of th a versi on dale(s) liste d below.
Soll SutveyAm Eisden County, North Carollna
SurveyA-ea Dula: Versicn 21, Sep 10. 2018
Sail map units are labeled (as space allows) for map scales
1:50,006 or larger.
Oate(s) aerial images were photograMod: Apr 22, 2095—Neu
28, 2617
The orthophoto or other base map on which the sail lines were
cprnplkid and fbgltlxe6 pnohably differs from the barkgmund
imagery6E;played on these maps. Asaresuft. some minor
Shifting d map unit boundaries may Ike a Adam.
Appendix B
B Project Area Photographs
Photo 1: View of Wetland 1 (seep) near the study area
facing southwest (02/27/19).
Photo 3: View of Wetland 1 (seep) near the study area
facing north (02/27/19).
Photo 5: View of road ditch near the study area facing south
that is not wet. Glengerry Road is visible on the left
(02/27/19).
Photo 2: View of Wetland 1 (seep) near the study area facing
north (02/27/19).
Photo 4: View of road ditch near the study area facing north
that is not wet. Glengerry Road is visible on the right
(02/27/19).
Photo 6: View of Wetland 2 (road ditch) near the study area
facing south where wetland plants become dominant.
Glengerry Road is visible on the left (02/27/19).
Photo 7: View of upstream end of Old Outfall 002 culvert
under Glengerry Road facing southeast (02/27/19).
Photo 9: View of UNT-1 to Cape Fear River showing Cape
Fear River backwater facing upstream (west) (02/27/19).
Photo 11: View of UNT-1 to Cape Fear River facing upstream
(02/27/19). This photo is west of the project area.
Photo 8: View of upstream end of Old Outfall 002 culvert
showing Cape Fear River backwater under Glengerry Road
facing southeast (02/27/19).
Photo 10: View of UNT-1 to Cape Fear River facing
downstream (east) (02/27/19).
Photo 12: View of UNT-2 to Cape Fear River facing upstream
(south) at confluence with UNT-1 to Cape Fear River
(02/27/19).
Photo 13: View of UNT-2 to Cape Fear River facing
downstream (north) at confluence with UNT-1 to Cape Fear
River (02/27/19).
Photo 15: View of typical upland habitat near the study
area where water treatment facility will be constructed
(02/27/19).
Photo 17: View of UNT-1 to Cape Fear River east of
Glengerry Road facing downstream (east) showing Cape
Fear River backwater (02/27/19). Not in project area.
Photo 14: View of ephemeral channel UNT-2 to Cape Fear
River facing upstream (south) (02/27/19).
Photo 16: View of UNT-1 to Cape Fear River facing
southwest with view of deeply incised banks and erosion
(02/27/19).
Photo 18: View of UNT-1 to Cape Fear River facing south
with view of deeply incised banks and erosion (02/27/19).
Photo 19. View of UNT-1 to Cape Fear River east of
Glengerry Road facing west showing normal stream flow
(05/07/19). Not in project area.
Photo 21: View of UNT-1 to Cape Fear River east of
Glengerry Road facing east toward the Cape Fear River
showing normal stream flow (05/07/19). This is downstream
from the project area.
Photo 23: View of upstream end of culvert under Glengerry
Road facing southeast during normal stream flow (05/07/19).
Photo 20: Upstream view of culvert under Glengerry Road
for UNT-1 to Cape Fear River east of Glengerry Road facing
west showing normal stream flow (05/07/19).
Photo 22: View of upstream end of culvert and retaining wall
under Glengerry Road facing downstream (east) during
normal stream flow (05/07/19).
Photo 24: Upstream view of UNT-1 facing west during
normal stream flow (05/07/19). This is in the affected project
area, just downstream from the proposed weir/instream
structure.
Appendix C
C Wetland Determination Data Forms
Sensitive / Proprietary#
Yes No
No Yes
No
No
No
No
Secondary Indicators (minimum of two required)
X
XX
Oxidized Rhizospheres on Living Roots (C3) Dry-Season Water Table (C2)
Saturation Visible on Aerial Imagery (C9)
X
Field Observations:
No
No
No Yes
02/27/19
WETLAND DETERMINATION DATA FORM - Atlantic and Gulf Coastal Plain Region
No
Section, Township, Range:
Are "normal circumstances" present?
Project/Site:
Subregion (LRR or MLRA):LRR: P; MLRA: 133A
Wagram fine sand, 0 to 6 percent slopes
The Chemour Company
significantly disturbed?
(If no, explain in Remarks.)
NA
Sampling Point:
ConcaveLocal relief (concave, convex, none):
X
Are climatic / hydrologic conditions on the site typical for this time of the year?
Landform (hillslope, terrace, etc.):
Datum:
Sampling Date:
, Soil
NA
0
Water-Stained Leaves (B9)
X
Yes
Hydrogen Sulfide Odor (C1)
Wetland Hydrology Present?
Sediment Deposits (B2)
Is the Sampled Area within a
Wetland?
Surface Soil Cracks (B6)
Sparsely Vegetated Concave Surface (B8)
Drainage Patterns (B10)
Moss Trim Lines (B16)
Presence of Reduced Iron (C4) Crayfish Burrows (C8)
Geomorphic Position (D2)
Inundation Visible on Aerial Imagery (B7)
X
X No
Other (Explain in Remarks)
Chemour Company
Luke F. Eggering, PWS
Depression
34.83262 -78.82661
Applicant/Owner:
Investigator(s):
Wetland Hydrology Indicators:
Yes
Are vegetation
Hydric Soil Present?
, or Hydrology
, or Hydrology
City/County:
State:NC
Bladen County
Soil Map Unit Name:NWI classification:
Slope (%):
Long:NAD 1983
(includes capillary fringe)
Depth (inches):
Yes Depth (inches):X No
Yes
X
X
Depth (inches):
Yes
XSurface water present?
Water table present?
Saturation present?
Saturation (A3)
Water Marks (B1)
Iron Deposits (B5)
Hydrophytic Vegetation Present?
HYDROLOGY
Yes
SUMMARY OF FINDINGS ̶ Attach site map showing sampling point locations, transects, important features, etc.
Are vegetation , Soil
Yes
Drift Deposits (B3)
High Water Table (A2)Marl Deposits (B15) (LRR U)
Surface Water (A1)
Primary Indicators (minimum of one is required; check all that apply)
Algal Mat or Crust (B4)
Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available:
Remarks:
The depression appears to remain saturated for long durations during the growing season. The soils are super saturated and were a slurry below 8
inches. A very strong hydrogen sulfide odor was observed.
Remarks:
This is a seep/depression in the ridge south of the stream (Old Outfall #2). The small area receives stormwater runoff and has groundwater to the
surface.
Wetland Hydrology Present?Surface
Wetland 1
Shallow Aquitard (D3)
Recent Iron Reduction in Tilled Soils (C6)
Thin Muck Surface (C7)
FAC-Neutral Test (D5)
Surface
Lat:
X
naturally problematic? (If needed, explain any answers in Remarks.)
X
Sphagnum moss (D8) (LRR T, U)
Aquatic Fauna (B13)
US Army Corps of Engineers Atlantic and Gulf Coastal Plain Region - Version 2.0
Sensitive / Proprietary#
)
1
2
3
4
5
6
7
8 Multiply by:
= Total Cover
)
1
2
3
4
5
6 Hydrophytic Vegetation Indicators:
7
8 X
= Total Cover
Problematic Hydrophytic Vegetation 1 (Explain)
)
1
2
3
4
5
6
7
8
9
10
11
12
= Total Cover
)
1
2
3
4
5
= Total Cover
Yes No
7
35
Herb Stratum
20% of total cover:
0
OBL species
FACW species x 2 =
0
Acer rubrum
FAC
FACU5
30 Y
2020% of total cover:5050% of total cover:
NFagus grandifolia
FAC species
FACU species
Prevalence Index worksheet
410
Number of Dominant Species
That Are OBL, FACW, or FAC:
0
20
x 3 =
x 4 =
3
Total Number of Dominant
Species Across all Strata:
Total % Cover of:
3
130
x 1 =100
X
0
20% of total cover:
0
The canopy is closed with virtually no understory species present.
0
20% of total cover:0
Remarks: (If observed, list morphological adaptations below).
0
1Indicators of hydric soil and wetland hydrology must be
present, unless disturbed or problematic.
5
VEGETATION (Four Strata) - Use scientific names of plants
Dominance Test worksheet:
FAC
Y
Sampling Point:
Absolute
% Cover
Dominant
Species?
Indicator
Status
60
Percent of Dominant Species that
are OBL, FACW, or FAC:
FAC40
Wetland 1
Tree Stratum
Sapliing/Shrub Stratum
(A)
(B)
(A/B)100.00%
390
0
0
(Plot Size:
(Plot Size:
YPinus taeda
Ilex opaca
50% of total cover:
50% of total cover:
50% of total cover:
(Plot Size:
(Plot Size:
17.5
Woody Vine Stratum
Hydrophytic
vegetation
present?
Tree - Woody plants, excluding vines 3 in. (7.6 cm) or more
in diameter at breast height (DBH), regardless of height.
Sapling/shrub - Woody plants, excluding vines, less than 3
in. DBH and greater than 3.28 ft (1 m) tall.
Herb - All herbaceous (non-woody) plants, regardless of
size, and woody plants less than 3.28 ft tall.
Woody vines - All woody vines greater than 3.28 ft in height.
Prevalence Index = B/A =
0
0
3 - Prevalence Index is ≤3.01
Definitions of Four Vegetation Strata:
1 -Rapid Test for Hydrophytic Vegetation
2 - Dominance Test is >50%
3.04
(B)135
x 5 =
(A)Column totals
UPL species
US Army Corps of Engineers Atlantic and Gulf Coastal Plain Region - Version 2.0
Sensitive / Proprietary#
5/2
3/1
Indicators for Problematic Hydric Soils3:
X
5 cm Mucky Mineral (A7) (LRR P, T, U)
Restrictive Layer (if observed):
Type:
Yes No
Color (moist)
Depth
(inches)
10YR
2.5Y 100
0-2
2-16
Matrix
%
100
RemarksType1
Redox Features
Texture
Silt loam
% Loc2Color (moist)
Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.)
Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.)
X
None
NA
Sandy loam Very loose/saturated
A lot of organic matter present
Histisol (A1)
Histic Epipedon (A2)
Black Histic (A3)
Polyvalue Below Surface (S8) (LRR S, T, U)
Thin Dark Surface (S9) (LRR, S, T, U)
Loamy Mucky Mineral (F1) (LRR O)
2Location: PL=Pore Lining, M=Matrix.1Type: C=Concentration, D=Depletion, RM=Reduced Matrix, CS=Covered or Coated Sand Grains.
Hydrogen Sulfide (A4)
Stratified Layers (A5)
Organic Bodies (A6) (LRR P, T, U)
Sandy Mucky Mineral (S1) (LRR O, S)
Remarks:
Below eight inches, soils were a super saturated slurry. The soil auger sunk through the slurry under its own weight.
Depth (inches):
Dark Surface (S7) (LRR P, S, T, U)
Muck Presence (A8) (LRR U)
1 cm Muck (A9) (LRR P, T)
Depleted Below Dark Suface (A11)
Thick Dark Surface (A12)
Coast Prairie Redox (A16) (MLRA 150A)
Redox Dark Surface (F6)
Delta Ochric (F17) (MLRA 151)
Very Shallow Dark Surface (TF12)
Other (Explain in Remarks)
3Indicators of hydrophytic vegetation and
wetland hydrology must be present,
unless disturbed or problematic.
Hydric soil present?
SOIL Sampling Point:Wetland 1
Piedmont Floodplain Soils (F19) (MLRA 149A)
Anomalous Bright Loamy Soils (F20) (MLRA 149A, 153C, 153D)
1 cm Muck (A9) (LRR O)
2 cm Muck (A10) (LRR S)
Reduced Vertic (F18) (outside MLRA 150A,B)
Piedmont Floodplain Soils (F19) (LRR P, S, T)
Anomalous Bright Loamy Soils (F20)
Reduced Vertic (F18) (MLRA 150A, 150B)
Redox Depressions (F8)
Sandy Gleyed Matrix (S4)
Sandy Redox (S5)
Stripped Matrix (S6)
Marl (F10) (LRR U)
Depleted Ochric (F11) (MLRA 151)
Iron-Manganese Masses (F12) (LRR O, P, T)
Umbric Surface (F13) (LRR P, T, U)
Loamy Gleyed Matrix (F2)
Depleted Matrix (F3)
(MLRA 153B)
Red Parent Material (TF2)Depleted Dark Surface (F7)
US Army Corps of Engineers Atlantic and Gulf Coastal Plain Region - Version 2.0
Sensitive / Proprietary#
Yes No
No Yes
No
No
No
No
Secondary Indicators (minimum of two required)
Oxidized Rhizospheres on Living Roots (C3) Dry-Season Water Table (C2)
Saturation Visible on Aerial Imagery (C9)
Field Observations:
No
No
No Yes
02/27/19
WETLAND DETERMINATION DATA FORM - Atlantic and Gulf Coastal Plain Region
No
Section, Township, Range:
Are "normal circumstances" present?
Project/Site:
Subregion (LRR or MLRA):LRR: P; MLRA: 133A
Wagram fine sand, 0 to 6 percent slopes
The Chemour Company
significantly disturbed?
(If no, explain in Remarks.)
NA
Sampling Point:
ConvexLocal relief (concave, convex, none):
X
Are climatic / hydrologic conditions on the site typical for this time of the year?
Landform (hillslope, terrace, etc.):
Datum:
Sampling Date:
, Soil
NA
10
Water-Stained Leaves (B9)
Yes
Hydrogen Sulfide Odor (C1)
Wetland Hydrology Present?
Sediment Deposits (B2)
Is the Sampled Area within a
Wetland?
Surface Soil Cracks (B6)
Sparsely Vegetated Concave Surface (B8)
Drainage Patterns (B10)
Moss Trim Lines (B16)
Presence of Reduced Iron (C4) Crayfish Burrows (C8)
Geomorphic Position (D2)
Inundation Visible on Aerial Imagery (B7)
X
No X
Other (Explain in Remarks)
Chemour Company
Luke F. Eggering, PWS
Hillslope
34.83250 -78.82663
Applicant/Owner:
Investigator(s):
Wetland Hydrology Indicators:
Yes
Are vegetation
Hydric Soil Present?
, or Hydrology
, or Hydrology
City/County:
State:NC
Bladen County
Soil Map Unit Name:NWI classification:
Slope (%):
Long:NAD 1983
(includes capillary fringe)
Depth (inches):
Yes Depth (inches):No
Yes
X
X
Depth (inches):
X
Yes
XSurface water present?
Water table present?
Saturation present?
Saturation (A3)
Water Marks (B1)
Iron Deposits (B5)
Hydrophytic Vegetation Present?
HYDROLOGY
Yes X
SUMMARY OF FINDINGS ̶ Attach site map showing sampling point locations, transects, important features, etc.
Are vegetation , Soil
Yes
Drift Deposits (B3)
High Water Table (A2)Marl Deposits (B15) (LRR U)
Surface Water (A1)
Primary Indicators (minimum of one is required; check all that apply)
Algal Mat or Crust (B4)
X
Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available:
Remarks:
The area is a moderately well-drained hillslope.
Remarks:
This is the upland point on a slope above Wetland 1 (seep/depression). It is well-drained within upland vegetation.
Wetland Hydrology Present?
Upland 1
Shallow Aquitard (D3)
Recent Iron Reduction in Tilled Soils (C6)
Thin Muck Surface (C7)
FAC-Neutral Test (D5)
Lat:
X
naturally problematic? (If needed, explain any answers in Remarks.)
Sphagnum moss (D8) (LRR T, U)
Aquatic Fauna (B13)
US Army Corps of Engineers Atlantic and Gulf Coastal Plain Region - Version 2.0
Sensitive / Proprietary#
)
1
2
3
4
5
6
7
8 Multiply by:
= Total Cover
)
1
2
3
4
5
6 Hydrophytic Vegetation Indicators:
7
8
= Total Cover
Problematic Hydrophytic Vegetation 1 (Explain)
)
1
2
3
4
5
6
7
8
9
10
11
12
= Total Cover
)
1
2
3
4
5
= Total Cover
Yes No
X
5
9
45
Herb Stratum
20% of total cover:
Ilex opaca
0
OBL species
FACW species x 2 =
0
Fagus grandifolia
FACU
20
20 Y
FACU
1720% of total cover:42.550% of total cover:
5Prunus caroliniana
YIpex opaca
FAC species
FACU species
Prevalence Index worksheet
455
Number of Dominant Species
That Are OBL, FACW, or FAC:
0
440
x 3 =
x 4 =
5
Total Number of Dominant
Species Across all Strata:
Total % Cover of:
1
5
N
x 1 =85
5
20% of total cover:
1
0
20% of total cover:0
Remarks: (If observed, list morphological adaptations below).
0
1Indicators of hydric soil and wetland hydrology must be
present, unless disturbed or problematic.
110
Y
VEGETATION (Four Strata) - Use scientific names of plants
Dominance Test worksheet:
FACU
Y
Sampling Point:
Absolute
% Cover
Dominant
Species?
Indicator
Status
60
Percent of Dominant Species that
are OBL, FACW, or FAC:
FACU25
Upland 1
Tree Stratum
Sapliing/Shrub Stratum
(A)
(B)
(A/B)20.00%
15
0
0
(Plot Size:
(Plot Size:
YAcer saccharum
Fagus grandifolia
50% of total cover:
50% of total cover:
50% of total cover:
(Plot Size:
(Plot Size:
22.5
Woody Vine Stratum
FAC
Hydrophytic
vegetation
present?
Tree - Woody plants, excluding vines 3 in. (7.6 cm) or more
in diameter at breast height (DBH), regardless of height.
Sapling/shrub - Woody plants, excluding vines, less than 3
in. DBH and greater than 3.28 ft (1 m) tall.
Herb - All herbaceous (non-woody) plants, regardless of
size, and woody plants less than 3.28 ft tall.
Woody vines - All woody vines greater than 3.28 ft in height.
Prevalence Index = B/A =
2.5
0
3 - Prevalence Index is ≤3.01
Definitions of Four Vegetation Strata:
1 -Rapid Test for Hydrophytic Vegetation
2 - Dominance Test is >50%
3.96
(B)115
x 5 =
(A)Column totals
UPL species
US Army Corps of Engineers Atlantic and Gulf Coastal Plain Region - Version 2.0
Sensitive / Proprietary#
6/2
5/4 /
Indicators for Problematic Hydric Soils3:
5 cm Mucky Mineral (A7) (LRR P, T, U)
Restrictive Layer (if observed):
Type:
Yes No
Color (moist)
Depth
(inches)
2
2.5Y
2.5Y 80
0-6
6-16
Matrix
%
6
100
Remarks
20
Type1
Redox Features
Texture
Sandy loam
2.5Y
% Loc2Color (moist)
Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.)
Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.)
X
None
NA
Sandy loam
Histisol (A1)
Histic Epipedon (A2)
Black Histic (A3)
Polyvalue Below Surface (S8) (LRR S, T, U)
Thin Dark Surface (S9) (LRR, S, T, U)
Loamy Mucky Mineral (F1) (LRR O)
2Location: PL=Pore Lining, M=Matrix.1Type: C=Concentration, D=Depletion, RM=Reduced Matrix, CS=Covered or Coated Sand Grains.
Hydrogen Sulfide (A4)
Stratified Layers (A5)
Organic Bodies (A6) (LRR P, T, U)
Sandy Mucky Mineral (S1) (LRR O, S)
Remarks:
The soils are fairly well drained on this slope above the wetland depression/seep. No hydrogen sulfide odor was observed.
Depth (inches):
Dark Surface (S7) (LRR P, S, T, U)
Muck Presence (A8) (LRR U)
1 cm Muck (A9) (LRR P, T)
Depleted Below Dark Suface (A11)
Thick Dark Surface (A12)
Coast Prairie Redox (A16) (MLRA 150A)
Redox Dark Surface (F6)
Delta Ochric (F17) (MLRA 151)
Very Shallow Dark Surface (TF12)
Other (Explain in Remarks)
3Indicators of hydrophytic vegetation and
wetland hydrology must be present,
unless disturbed or problematic.
Hydric soil present?
SOIL Sampling Point:Upland 1
Piedmont Floodplain Soils (F19) (MLRA 149A)
Anomalous Bright Loamy Soils (F20) (MLRA 149A, 153C, 153D)
1 cm Muck (A9) (LRR O)
2 cm Muck (A10) (LRR S)
Reduced Vertic (F18) (outside MLRA 150A,B)
Piedmont Floodplain Soils (F19) (LRR P, S, T)
Anomalous Bright Loamy Soils (F20)
Reduced Vertic (F18) (MLRA 150A, 150B)
Redox Depressions (F8)
Sandy Gleyed Matrix (S4)
Sandy Redox (S5)
Stripped Matrix (S6)
Marl (F10) (LRR U)
Depleted Ochric (F11) (MLRA 151)
Iron-Manganese Masses (F12) (LRR O, P, T)
Umbric Surface (F13) (LRR P, T, U)
Loamy Gleyed Matrix (F2)
Depleted Matrix (F3)
(MLRA 153B)
Red Parent Material (TF2)Depleted Dark Surface (F7)
US Army Corps of Engineers Atlantic and Gulf Coastal Plain Region - Version 2.0
Sensitive / Proprietary#
Yes No
No Yes
No
No
No
No
Secondary Indicators (minimum of two required)
X
Oxidized Rhizospheres on Living Roots (C3) Dry-Season Water Table (C2)
Saturation Visible on Aerial Imagery (C9)
Field Observations:
No
No
No Yes
Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available:
Remarks:
The road-side ditch appears to remain saturated for long durations during the growing season. Filamentous algae was observed in inundated
portions of the ditch. Seep water emerges from adjacent uplands in two or three areas along the road ditch.
Remarks:
This is a small road ditch wetland along Glengerry Road. The small area receives stormwater runoff and appears to receive seep water from the
adjacent uplands.
Wetland Hydrology Present?
up to 2"
surface
Wetland 2
Shallow Aquitard (D3)
Recent Iron Reduction in Tilled Soils (C6)
Thin Muck Surface (C7)
FAC-Neutral Test (D5)
Lat:
X
naturally problematic? (If needed, explain any answers in Remarks.)
X
Sphagnum moss (D8) (LRR T, U)
Aquatic Fauna (B13)
Saturation (A3)
Water Marks (B1)
Iron Deposits (B5)
Hydrophytic Vegetation Present?
HYDROLOGY
Yes
SUMMARY OF FINDINGS ̶ Attach site map showing sampling point locations, transects, important features, etc.
Are vegetation , Soil
Yes
Drift Deposits (B3)
High Water Table (A2)Marl Deposits (B15) (LRR U)
Surface Water (A1)
Primary Indicators (minimum of one is required; check all that apply)
Algal Mat or Crust (B4)
(includes capillary fringe)
Depth (inches):
Yes Depth (inches):X No
Yes
X
X
X Depth (inches):
Yes
Surface water present?
Water table present?
Saturation present?
Chemour Company
Luke F. Eggering, PWS
Depression
34.83447 -78.82595
Applicant/Owner:
Investigator(s):
Wetland Hydrology Indicators:
Yes
Are vegetation
Hydric Soil Present?
, or Hydrology
, or Hydrology
City/County:
State:NC
Bladen County
Soil Map Unit Name:NWI classification:
Slope (%):
Long:NAD 1983
NA
2
Water-Stained Leaves (B9)
X
Yes
Hydrogen Sulfide Odor (C1)
Wetland Hydrology Present?
Sediment Deposits (B2)
Is the Sampled Area within a
Wetland?
Surface Soil Cracks (B6)
Sparsely Vegetated Concave Surface (B8)
Drainage Patterns (B10)
Moss Trim Lines (B16)
Presence of Reduced Iron (C4) Crayfish Burrows (C8)
Geomorphic Position (D2)
Inundation Visible on Aerial Imagery (B7)
X
X No
Other (Explain in Remarks)
02/27/19
WETLAND DETERMINATION DATA FORM - Atlantic and Gulf Coastal Plain Region
No
Section, Township, Range:
Are "normal circumstances" present?
Project/Site:
Subregion (LRR or MLRA):LRR: P; MLRA: 133A
Dystrochrepts, steep
The Chemour Company
significantly disturbed?
(If no, explain in Remarks.)
NA
Sampling Point:
ConcaveLocal relief (concave, convex, none):
X
Are climatic / hydrologic conditions on the site typical for this time of the year?
Landform (hillslope, terrace, etc.):
Datum:
Sampling Date:
, Soil
US Army Corps of Engineers Atlantic and Gulf Coastal Plain Region - Version 2.0
Sensitive / Proprietary#
)
1
2
3
4
5
6
7
8 Multiply by:
= Total Cover
)
1
2
3
4
5
6 Hydrophytic Vegetation Indicators:
7 X
8
= Total Cover
Problematic Hydrophytic Vegetation 1 (Explain)
)
1
2
3
4
5
6
7
8
9
10
11
12
= Total Cover
)
1
2
3
4
5
= Total Cover
Yes No
Hydrophytic
vegetation
present?
Tree - Woody plants, excluding vines 3 in. (7.6 cm) or more
in diameter at breast height (DBH), regardless of height.
Sapling/shrub - Woody plants, excluding vines, less than 3
in. DBH and greater than 3.28 ft (1 m) tall.
Herb - All herbaceous (non-woody) plants, regardless of
size, and woody plants less than 3.28 ft tall.
Woody vines - All woody vines greater than 3.28 ft in height.
Prevalence Index = B/A =
42.5
0
3 - Prevalence Index is ≤3.01
Definitions of Four Vegetation Strata:
1 -Rapid Test for Hydrophytic Vegetation
2 - Dominance Test is >50%
(B)
x 5 =
(A)Column totals
UPL species
50% of total cover:
50% of total cover:
50% of total cover:
(Plot Size:
(Plot Size:
Carex spp.
0
Woody Vine Stratum
5N
OBL
Wetland 2
Tree Stratum
Sapliing/Shrub Stratum
(A)
(B)
(A/B)
(Plot Size:
(Plot Size:
VEGETATION (Four Strata) - Use scientific names of plants
Dominance Test worksheet:
Sampling Point:
Absolute
% Cover
Dominant
Species?
Indicator
Status
Percent of Dominant Species that
are OBL, FACW, or FAC:
1Indicators of hydric soil and wetland hydrology must be
present, unless disturbed or problematic.
Y
Remarks: (If observed, list morphological adaptations below).
The canopy is open. The Carex spp. was mowed and could not be identified ot species. There was woolgrass (Scirpus cyperinus) in the road ditch
approximately 40 yards north of the sample point. Filamentous algae was present in several locations along the road ditch.
0
20% of total cover:0 X
85
20% of total cover:17
FAC species
FACU species
Prevalence Index worksheet
Number of Dominant Species
That Are OBL, FACW, or FAC:
x 3 =
x 4 =
Total Number of Dominant
Species Across all Strata:
Total % Cover of:
x 1 =0 OBL species
FACW species x 2 =020% of total cover:050% of total cover:
80
0
0
Herb Stratum
20% of total cover:
Juncus effusus
US Army Corps of Engineers Atlantic and Gulf Coastal Plain Region - Version 2.0
Sensitive / Proprietary#
5/2
3/1
Indicators for Problematic Hydric Soils3:
X
5 cm Mucky Mineral (A7) (LRR P, T, U)
Restrictive Layer (if observed):
Type:
Yes No
SOIL Sampling Point:Wetland 2
Piedmont Floodplain Soils (F19) (MLRA 149A)
Anomalous Bright Loamy Soils (F20) (MLRA 149A, 153C, 153D)
1 cm Muck (A9) (LRR O)
2 cm Muck (A10) (LRR S)
Reduced Vertic (F18) (outside MLRA 150A,B)
Piedmont Floodplain Soils (F19) (LRR P, S, T)
Anomalous Bright Loamy Soils (F20)
Reduced Vertic (F18) (MLRA 150A, 150B)
Redox Depressions (F8)
Sandy Gleyed Matrix (S4)
Sandy Redox (S5)
Stripped Matrix (S6)
Marl (F10) (LRR U)
Depleted Ochric (F11) (MLRA 151)
Iron-Manganese Masses (F12) (LRR O, P, T)
Umbric Surface (F13) (LRR P, T, U)
Loamy Gleyed Matrix (F2)
Depleted Matrix (F3)
(MLRA 153B)
Red Parent Material (TF2)Depleted Dark Surface (F7)
Hydrogen Sulfide (A4)
Stratified Layers (A5)
Organic Bodies (A6) (LRR P, T, U)
Sandy Mucky Mineral (S1) (LRR O, S)
Remarks:
Soils are a sandy loam that are saturated to the surface. Soils were inundated up to two inches in some portions of the wetland.
Depth (inches):
Dark Surface (S7) (LRR P, S, T, U)
Muck Presence (A8) (LRR U)
1 cm Muck (A9) (LRR P, T)
Depleted Below Dark Suface (A11)
Thick Dark Surface (A12)
Coast Prairie Redox (A16) (MLRA 150A)
Redox Dark Surface (F6)
Delta Ochric (F17) (MLRA 151)
Very Shallow Dark Surface (TF12)
Other (Explain in Remarks)
3Indicators of hydrophytic vegetation and
wetland hydrology must be present,
unless disturbed or problematic.
Hydric soil present?
Histisol (A1)
Histic Epipedon (A2)
Black Histic (A3)
Polyvalue Below Surface (S8) (LRR S, T, U)
Thin Dark Surface (S9) (LRR, S, T, U)
Loamy Mucky Mineral (F1) (LRR O)
2Location: PL=Pore Lining, M=Matrix.1Type: C=Concentration, D=Depletion, RM=Reduced Matrix, CS=Covered or Coated Sand Grains.
Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.)
Hydric Soil Indicators: (Applicable to all LRRs, unless otherwise noted.)
X
None
NA
Sandy loam
RemarksType1
Redox Features
Texture
Sandy loam
% Loc2Color (moist)Color (moist)
Depth
(inches)
10YR
2.5Y 100
0-2
2-16
Matrix
%
100
US Army Corps of Engineers Atlantic and Gulf Coastal Plain Region - Version 2.0
Appendix D
D Stream Data Forms
NC Division of Water Quality –Methodology for Identification of Intermittent and
Perennial Streams and Their Origins v. 4.11
NC DWQ Stream Identification Form Version 4.11
Date: Project/Site: Latitude:
Evaluator: County: Longitude:
Total Points:
Stream is at least intermittent
if ≥ 19 or perennial if ≥ 30*
Stream Determination (circle one)
Ephemeral Intermittent Perennial
Other
e.g. Quad Name:
A. Geomorphology (Subtotal =_________) Absent Weak Moderate Strong
1a. Continuity of channel bed and bank 0 1 2 3
2. Sinuosity of channel along thalweg 0 1 2 3
3. In-channel structure: ex. riffle-pool, step-pool,
ripple-pool sequence 0 1 2 3
4. Particle size of stream substrate 0 1 2 3
5. Active/relict floodplain 0 1 2 3
6. Depositional bars or benches 0 1 2 3
7. Recent alluvial deposits 0 1 2 3
8. Headcuts 0 1 2 3
9. Grade control 0 0.5 1 1.5
10. Natural valley 0 0.5 1 1.5
11. Second or greater order channel No = 0 Yes = 3
a artificial ditches are not rated; see discussions in manual
B. Hydrology (Subtotal = _________)
12. Presence of Baseflow 0 1 2 3
13. Iron oxidizing bacteria 0 1 2 3
14. Leaf litter 1.5 1 0.5 0
15. Sediment on plants or debris 0 0.5 1 1.5
16. Organic debris lines or piles 0 0.5 1 1.5
17. Soil-based evidence of high water table?No = 0 Yes = 3
C. Biology (Subtotal = _________)
18. Fibrous roots in streambed 3 2 1 0
19. Rooted upland plants in streambed 3 2 1 0
20. Macrobenthos (note diversity and abundance)0 1 2 3
21. Aquatic Mollusks 0 1 2 3
22. Fish 0 0.5 1 1.5
23. Crayfish 0 0.5 1 1.5
24. Amphibians 0 0.5 1 1.5
25. Algae 0 0.5 1 1.5
26. Wetland plants in streambed FACW = 0.75 OBL = 1.5 Other = 0
Notes:
Sketch: N
Glengerry RoadHeadwall Headwall
Fill Fill
12-foot Culvert
NC Division of Water Quality –Methodology for Identification of Intermittent and
Perennial Streams and Their Origins v. 4.11
NC DWQ Stream Identification Form Version 4.11
Date: Project/Site: Latitude:
Evaluator: County: Longitude:
Total Points:
Stream is at least intermittent
if ≥ 19 or perennial if ≥ 30*
Stream Determination (circle one)
Ephemeral Intermittent Perennial
Other
e.g. Quad Name:
A. Geomorphology (Subtotal =_________) Absent Weak Moderate Strong
1a. Continuity of channel bed and bank 0 1 2 3
2. Sinuosity of channel along thalweg 0 1 2 3
3. In-channel structure: ex. riffle-pool, step-pool,
ripple-pool sequence 0 1 2 3
4. Particle size of stream substrate 0 1 2 3
5. Active/relict floodplain 0 1 2 3
6. Depositional bars or benches 0 1 2 3
7. Recent alluvial deposits 0 1 2 3
8. Headcuts 0 1 2 3
9. Grade control 0 0.5 1 1.5
10. Natural valley 0 0.5 1 1.5
11. Second or greater order channel No = 0 Yes = 3
a artificial ditches are not rated; see discussions in manual
B. Hydrology (Subtotal = _________)
12. Presence of Baseflow 0 1 2 3
13. Iron oxidizing bacteria 0 1 2 3
14. Leaf litter 1.5 1 0.5 0
15. Sediment on plants or debris 0 0.5 1 1.5
16. Organic debris lines or piles 0 0.5 1 1.5
17. Soil-based evidence of high water table?No = 0 Yes = 3
C. Biology (Subtotal = _________)
18. Fibrous roots in streambed 3 2 1 0
19. Rooted upland plants in streambed 3 2 1 0
20. Macrobenthos (note diversity and abundance)0 1 2 3
21. Aquatic Mollusks 0 1 2 3
22. Fish 0 0.5 1 1.5
23. Crayfish 0 0.5 1 1.5
24. Amphibians 0 0.5 1 1.5
25. Algae 0 0.5 1 1.5
26. Wetland plants in streambed FACW = 0.75 OBL = 1.5 Other = 0
Notes:
Sketch: N
Glengerry RoadHeadwall Headwall
Fill Fill
12-foot Culvert
UNT-2 to Cape Fear River
UNT-1 to Cape Fear River
NC Division of Water Quality –Methodology for Identification of Intermittent and
Perennial Streams and Their Origins v. 4.11
NC DWQ Stream Identification Form Version 4.11
Date: Project/Site: Latitude:
Evaluator: County: Longitude:
Total Points:
Stream is at least intermittent
if ≥ 19 or perennial if ≥ 30*
Stream Determination (circle one)
Ephemeral Intermittent Perennial
Other
e.g. Quad Name:
A. Geomorphology (Subtotal =_________) Absent Weak Moderate Strong
1a. Continuity of channel bed and bank 0 1 2 3
2. Sinuosity of channel along thalweg 0 1 2 3
3. In-channel structure: ex. riffle-pool, step-pool,
ripple-pool sequence 0 1 2 3
4. Particle size of stream substrate 0 1 2 3
5. Active/relict floodplain 0 1 2 3
6. Depositional bars or benches 0 1 2 3
7. Recent alluvial deposits 0 1 2 3
8. Headcuts 0 1 2 3
9. Grade control 0 0.5 1 1.5
10. Natural valley 0 0.5 1 1.5
11. Second or greater order channel No = 0 Yes = 3
a artificial ditches are not rated; see discussions in manual
B. Hydrology (Subtotal = _________)
12. Presence of Baseflow 0 1 2 3
13. Iron oxidizing bacteria 0 1 2 3
14. Leaf litter 1.5 1 0.5 0
15. Sediment on plants or debris 0 0.5 1 1.5
16. Organic debris lines or piles 0 0.5 1 1.5
17. Soil-based evidence of high water table?No = 0 Yes = 3
C. Biology (Subtotal = _________)
18. Fibrous roots in streambed 3 2 1 0
19. Rooted upland plants in streambed 3 2 1 0
20. Macrobenthos (note diversity and abundance)0 1 2 3
21. Aquatic Mollusks 0 1 2 3
22. Fish 0 0.5 1 1.5
23. Crayfish 0 0.5 1 1.5
24. Amphibians 0 0.5 1 1.5
25. Algae 0 0.5 1 1.5
26. Wetland plants in streambed FACW = 0.75 OBL = 1.5 Other = 0
Notes:
Sketch: N
Glengerry RoadCulvert
UNT-3 to Cape Fear River
UNT-3 to Cape Fear River