20170905 Ver 2_NCWAM - Wetland D_20180509

NC WAM WETLAND ASSESSMENT FORM
Accompanies User Manual Version 5
USACE AID#: NCDWR #:
Project Name Graham Drive In (SAW -2017-01582) Date of Evaluation 4/10/2018
Applicant/Owner Name Chuck Talley Wetland Site Name Wetland D (from SAW -2016-02023)
Wetland Type Headwater Forest Assessor Name/Organization David Bailey (USAGE)
Level III Ecoregion Piedmont Nearest Named Water Body Back Creek
River Basin Cape Fear USGS 8 -Digit Catalogue Unit 03030002
County Alamance NCDWR Region
E;

4. Soil Texture/Structure - assessment area condition metric (skip for all marshes)
Check a box from each of the three soil property groups below. Dig soil profile in the dominant assessment area landscape
feature. Make soil observations within the 12 inches. Use most recent National Technical Committee for Hydric Soils guidance for
regional indicators.
4a. A Sandy soil
B Loamy or clayey soils exhibiting redoximorphic features (concentrations, depletions, or rhizospheres)
C Loamy or clayey soils not exhibiting redoximorphic features
D Loamy or clayey gleyed soil
E Histosol or histic epipedon
4b.;A Soil ribbon < 1 inch
[; B Soil ribbon >- 1 inch
4c. [;A No peat or muck presence
B A peat or muck presence
5. Discharge into Wetland - opportunity metric
Check a box in each column. Consider surface pollutants or discharges (Surf) and sub -surface pollutants or discharges (Sub).
Examples of sub -surface discharges include presence of nearby septic tank, underground storage tank (UST), etc.
Surf Sub
�A A Little or no evidence of pollutants or discharges entering the assessment area
B B Noticeable evidence of pollutants or discharges entering the wetland and stressing, but not overwhelming the
treatment capacity of the assessment area
C C Noticeable evidence of pollutants or discharges (pathogen, particulate, or soluble) entering the assessment area and
potentially overwhelming the treatment capacity of the wetland (water discoloration, dead vegetation, excessive
sedimentation, odor)
6. Land Use - opportunity metric (skip for non -riparian wetlands)
Check all that apply (at least one box in each column). Evaluation involves a GIS effort with field adjustment. Consider sources
draining to assessment area within entire upstream watershed (WS), within 5 miles and within the watershed draining to the
assessment area (5M), and within 2 miles and within the watershed draining to the assessment area (2M). Effective riparian buffers
are considered to be 50 feet wide in the Coastal Plain and Piedmont ecoregions and 30 feet wide in the Blue Ridge Mountains ecoregion.
WS 5M 2M
r A F A r A >- 10% impervious surfaces
f✓ B f✓ B r B Confined animal operations (or other local, concentrated source of pollutants)
r C r C r- C >- 20% coverage of pasture
F D r D i D >- 20% coverage of agricultural land (regularly plowed land)
F_1 E 1`71 E R E >- 20% coverage of maintained grass/herb
F_ F r F r F >- 20% coverage of clear-cut land
F G r- G i- G Little or no opportunity to improve water quality. Lack of opportunity may result from little or no disturbance in
the watershed or hydrologic alterations that prevent dainage and/or overbank flow from affectio the
assessment area.
7. Wetland Acting as Vegetated Buffer- assessment area/wetland complex condition metric (skip for non -riparian wetlands)
7a. Is assessment area within 50 feet of a tributary or other open water?
;Yes r;No If Yes, continue to 7b. If No, skip to Metric 8.
7b. How much of the first 50 feet from the bank is weltand? (Wetland buffer need only be present on one side of the water body. Make
buffer judgment based on the average width of wetland. Record a note if a portion of the buffer has been removed or disturbed.)
A >- 50 feet
B From 30 to < 50 feet
C From 15 to < 30 feet
D From 5 to < 15 feet
E < 5 feet or buffer bypassed by ditches
7c. Tributary width. If the tributary is anastomosed, combine widths of channels/braids for a total width.
F,:5 15 -feet wide r; > 15 -feet wide r; Other open water (no tributary present)
7d. Do roots of assessment area vegetation extend into the bank of the tributary/open water?
r; Yes F, No
7e. Is tributary or other open water sheltered or exposed?
Sheltered - adjacent open water with width < 2500 feet and no regular boat traffic.
Exposed - adjacent open water with width >_ 2500 feet or regular boat traffic.
8. Wetland Width at the Assessment Area - wetland type/wetland complex condition metric (evaluate WT for all marshes
and Estuarine Woody Wetland only; evaluate WC for Bottomland Hardwood Forest, Headwater Forest, and Riverine Swamp
Forest only)
Check a box in each column. Select the average width for the wetland type at the assessment area (WT) and the wetland complex at the
assessment area (WC). See User Manual for WT and WC boundaries.
WT WC
A A > 100 feet
B B From 80 to < 100 feet
C C From 50 to < 80 feet
D D From 40 to < 50 feet
E E From 30 to < 40 feet
F; F From 15 to < 30 feet
G G From 5 to < 15 feet
�; H H < 5 feet

9. Inundation Duration — assessment area condition metric (skip for non -riparian wetlands)
Answer for assessment area dominant landform.
A Evidence of short -duration inundation (< 7 consecutive days)
B Evidence of saturation, without evidence of inundation
C Evidence of long -duration inundation or very long -duration inundation (7 to 30 consecutive days or more)
10. Indicators of Deposition — assessment area condition metric (skip for non -riparian wetlands and all marshes)
Consider recent deposition only (no plant growth since deposition).
A Sediment deposition is not excessive, but at approximately natural levels.
B Sediment deposition is excessive, but not overwhelming the wetland.
C Sediment deposition is excessive and is overwhelming the wetland.
11. Wetland Size — wetland type/wetland complex condition metric
Check a box in each column. Involves a GIS effort with field adjustment. This metric evaluates three aspects of the wetland area: the
size of the wetland type (WT), the size of the wetland complex (WC), and the size of the forested wetland (FW) (if applicable, see User
Manual). See the User Manual for boundaries of these evaluation areas. If assessment area is clear-cut, select "K" for the FW column.
WT WC FW (if applicable)
CA CA CA >_ 500 acres
CB CB []B From 100 to < 500 acres
CC CC L]C From 50 to < 100 acres
CD C D L� D From 25 to < 50 acres
CE CE L] E From 10 to < 25 acres
CF C F C F From 5 to < 10 acres
CG CG L]G From 1 to < 5 acres
CH CH L]H From 0.5 to < 1 acre
C I C I L] I From 0.1 to < 0.5 acre
EJ E;J EJ From 0.01 to < 0.1 acre
CK E]K CK < 0.01 acre or assessment area is clear-cut
12. Wetland Intactness — wetland type condition metric (evaluate for Pocosins only)
CA Pocosin is the full extent (>_ 90%) of its natural landscape size.
CB Pocosin is < 90% of the full extent of its natural landscape size.
13. Connectivity to Other Natural Areas — landscape condition metric
13a. Check appropriate box(es) (a box may be checked in each column). Involves a GIS effort with field adjustment. This
evaluates whether the wetland is well connected (Well) and/or loosely connected (Loosely) to the landscape patch, the contiguous
metric naturally vegetated area and open water (if appropriate). Boundaries are formed by four -lane roads, regularly maintained utility
line corridors the width of a four -lane road or wider, urban landscapes, fields (pasture open and agriculture), or water > 300 feet wide.
Well Loosely
CA EA >_ 500 acres
CB E B From 100 to < 500 acres
EC E C From 50 to < 100 acres
CD E D From 10 to < 50 acres
CE CE < 10 acres
C F C F Wetland type has a poor or no connection to other natural habitats
13b. Evaluate for marshes only.
CYes C No Wetland type has a surface hydrology connection to open waters/stream or tidal wetlands.
14. Edge Effect — wetland type condition metric (skip for all marshes and Estuarine Woody Wetland)
May involve a GIS effort with field adjustment. Estimate distance from wetland type boundary to artificial edges. Artificial edges include
non -forested areas >_ 40 feet wide such as fields, development, roads, regularly maintained utility line corridors and clear -cuts. Consider
the eight main points of the compass. Artificial edge occurs within 150 feet in how many directiions? If the assessment area is clear-cut,
select option "C."
CA 0
CB 1 to
EC 5to8
15. Vegetative Composition — assessment area condition metric (skip for all marshes and Pine Flat)
CA Vegetation is close to reference condition in species present and their proportions. Lower strata composed of appropriate
species, with exotic plants absent or sparse within the assessment area.
EB Vegetation is different from reference condition in species diversity or proportions, but still largely composed of native species
characteristic of the wetland type. This may include communities of weedy native species that develop after clearcutting or
clearing. It also includes communities with exotics present, but not dominant, over a large portion of the expected strata.
CC Vegetation severely altered from reference in composition, or expected species are unnaturally absent (planted stands of non -
characteristic species or at least one stratum inappropriately composed of a single species), or exotic species are dominant in
at least one stratum.
16. Vegetative Diversity — assessment area condition metric (evaluate for Non -tidal Freshwater Marsh only)
CA Vegetation diversity is high and is composed primarily of native species (<10% cover of exotics).
EB Vegetation diversity is low or has > 10% to 50% cover of exotics.
CC Vegetation is dominated by exotic species (>50% cover of exotics).

17. Vegetative Structure — assessment area/wetland type condition metric
17a. Is vegetation present?
E Yes C: No If Yes, continue to 17b. If No, skip to Metric 18.
17b. Evaluate percent coverage of assessment area vegetation for all marshes only. Skip to 17c for non -marsh wetlands.
E;A
>_ 25%
coverage of vegetation
C B
< 25%
coverage of vegetation
17c. Check a box in each column for each stratum. Evaluate this portion of the metric for non -marsh wetlands. Consider structure
in airspace
above the assessment area (AA) and the wetland type (WT) separately.
AA
WT
o
[:A
[:A
Canopy closed, or nearly closed, with natural gaps associated with natural processes
C
E; B
E; B
Canopy present, but opened more than natural gaps
v
[:C
[:C
Canopy sparse or absent
o
[:A
[:A
Dense mid-story/sapling layer
E;B
E;B
Moderate density mid-story/sapling layer
[:C
[:C
Mid-story/sapling layer sparse or absent
a
[:A
[:A
Dense shrub layer
t
[:B
[:B
Moderate density shrub layer
E;C
E;C
Shrub layer sparse or absent
[:A
[:A
Dense herb layer
B
[:B
Moderate density herb layer
C
E;C
Herb layer sparse or absent
18. Snags — wetland type condition metric (skip for all marshes)
[:A Large snags (more than one) are visible (> 12 -inches DBH, or large relative to species present and landscape stability).
EB Not
19. Diameter Class Distribution — wetland type condition metric (skip for all marshes)
[]A Majority of canopy trees have stems > 6 inches in diameter at breast height (DBH); many large trees (> 12 inches DBH) are
present.
B Majority of canopy trees have stems between 6 and 12 inches DBH, few are > 12 -inch DBH.
C Majority of canopy trees are < 6 inches DBH or no trees.
20. Large Woody Debris — wetland type condition metric (skip for all marshes)
Include both natural debris and man -placed natural debris.
[:A Large logs (more than one) are visible (> 12 inches in diameter, or large relative to species present and landscape stability).
EB Not
21. Vegetation/Open Water Dispersion — wetland type/open water condition metric (evaluate for Non -Tidal Freshwater
Marsh only)
Select the figure that best describes the amount of interspersion between vegetation and open water in the growing season. Patterned
areas indicate vegetated areas, while solid white areas indicate open water.
[:A EB EC [:D
-•=.:� ; � "�..�, 1. �--r
22. Hydrologic Connectivity — assessment area condition metric (evaluate for riparian wetlands and Salt/Brackish Marsh only)
Examples of activities that may severely alter hydrologic connectivity include intensive ditching, fill, sedimentation, channelization,
diversion, man-made berms, beaver dams, and stream incision. Documentation required if evaluated as B, C, or D.
[:A Overbank and overland flow are not severely altered in the assessment area.
B Overbank flow is severely altered in the assessment area.
[:C Overland flow is severely altered in the assessment area.
D Both overbank and overland flow are severely altered in the assessment area.
Notes
Site is upper reaches of a natural drainage way cut off by a haul road in early1990s. Site may have also been used as a sediment basin for asphalt
plant in 1990s, although the area has naturalized. This wetland ponds water —1-2 feet deep following rain events. A culvert pipe exists under the haul
road, but the invert is set 1-2' higher than the lowest elevation section of the wetland. The concentrated pollutants for item # 6 refers to the asphalt plant
property (now abandoned) located directly uphill of wetland D. This area leaches petrochemical runoff and leachate into the assessment area. Wetland
D is seperated from the nearest tributary by a road, which explains the very small amount of wetland within 50 feet of the nearest tributary. Overland
flow to Wetland D has been altered severly due to grading from 1990s asphalt plant. Overbank flow from nearest tributary does not reach wetland due
to road and culvert pipe seperating wetland from stream.

NC WAM Wetland Rating Sheet
Accompanies User Manual
Version 5.0
Wetland Site Name Wetland D (from SAW -2016-02023)
Date
4/10/2018
Wetland Type Headwater Forest
Assessor Name/Organization
David Bailey (USACE)
Notes on Field Assessment Form (Y/N)
YES
Presence of regulatory considerations (Y/N)
YES
Wetland is intensively managed (Y/N)
NO
Assessment area is located within 50 feet of a natural tributary or other open
water (Y/N)
YES
Assessment area is substantially altered by beaver (Y/N)
NO
Assessment area experiences overbank flooding during normal rainfall conditions (Y/N)
NO
Assessment area is on a coastal island (Y/N)
NO
Sub -function Rating Summary
Function Sub -function
Metrics
Rating
Hydrology Surface Storage and Retention
Condition
LOW
Sub -Surface Storage and Retention
Condition
MEDIUM
Water Quality Pathogen Change
Condition
LOW
Condition/Opportunity
LOW
Opportunity Presence? (Y/N)
NO
Particulate Change
Condition
LOW
Condition/Opportunity
NA
Opportunity Presence? (Y/N)
NA
Soluble Change
Condition
LOW
Condition/Opportunity
LOW
Opportunity Presence? (Y/N)
NO
Physical Change
Condition
LOW
Condition/Opportunity
LOW
Opportunity Presence? (Y/N)
NO
Pollution Change
Condition
NA
Condition/Opportunity
NA
Opportunity Presence? (Y/N)
NA
Habitat Physical Structure
Condition
MEDIUM
Landscape Patch Structure
Condition
LOW
Vegetation Composition
Condition
MEDIUM
Function Rating Summary
Function Metrics/Notes
Rating
Hydrology Condition
LOW
Water Quality Condition
LOW
Condition/Opportunity
LOW
Opportunity Presence? (Y/N)
NO
Habitat Condition
LOW
Overall Wetland Rating LOW