3.3
Cape
Fear River Subbasin 03-06-16
Includes the Cape Fear River, Harrison Creek and Turnbull Creek
Municipalities: City of Elizabethtown
LCFRP
Station Codes (DWQ #): BRN (66),
HAM (67), NC11 (59)
DWQ/UNCW ambient monitoring site(s): NC11
Waterbody: Lower Cape Fear River
Location: Within
Bladen County, Browns and Hammonds Creeks are near Elizabethtown.
NC11 is on the main stem of the Cape Fear River
Lat/Lon: N
34.56853 W 78.55147
(BRN) to
N 34.39663
W 78.26785 (NC11)
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Use Support Ratings, from NCDENR, DWQ (2000 Basinwide
Report):
Fully Supporting:
240.8 mi.
Partially Supporting:
0.0 mi.
Not Supporting:
8.5 mi.
Not Rated:
11.8 mi.
The portion of the Cape Fear River within this subbasin is
deep and slow moving. There are
several natural lakes and streams that are tannin-stained with low pH
blackwaters. Land use is mostly
forest and marsh with some agriculture within the subbasin.
There are eight permitted dischargers, mostly near Elizabethtown.
Four of the largest dischargers, Veeder-Root, Smithfield Foods
Incorporated in Tar Heel, Alamac Knit Fabrics in Elizabethtown, and Dupont of
Fayetteville, discharge directly into the Cape Fear River.
(NCDENR, DWQ Cape Fear River Basinwide Water Quality Plan, July 2000)
Portions of Turnbull Creek and Harrisons Creek were
considered partially supporting (PS) in the 1996 Basinwide Plan.
Both are currently fully supporting (FS) and no longer on the state’s
303(d) list. Browns Creek (8.5
miles from source to Cape Fear River) is non supporting (NS) according to recent
DWQ monitoring because of an impaired biological community.
Urban nonpoint sources and sanitary sewer overflows from the City of
Elizabethtown are possible sources of impairment. This stream is on the state’s year 2000 303(d) list.
(NCDENR, DWQ Cape Fear River Basinwide Water Quality Plan, July 2000)
Approximately 1% of the waters in this subbasin are
impaired by nonpoint source pollution (mostly urban).
All of the waters in this subbasin are affected by nonpoint sources.
DENR, other state agencies and environmental groups have programs and
initiatives underway to address water quality problems associated with nonpoint
sources. (NCDENR, DWQ Cape Fear
River Basinwide Water Quality Plan, July 2000)
UNC-Wilmington
– Center for Marine Science, LCFRP
Station Names: BRN, HAM, NC11
Data collection: NC11 since June
1995, BRN & HAM since February 1996
Sampling relevance: NC11 represents
water entering the Lower Cape Fear River watershed from the middle basin.
There are also several concentrated animal operations within the area.


NC11
- main stem of Cape Fear
River, deep channel, relatively slow
moving, freshwater yet tidally influenced
The sites at Browns Creek (BRN) and North Carolina Highway 11
(NC11) were found to have a good quality rating for dissolved oxygen, meeting
the North Carolina State Standard of 5.0 mg/L in all sampled months.
Hammonds Creek (HAM), a small channelized tributary, was rated as poor,
with dissolved oxygen levels falling below 5.0 mg/L in four of the twelve
sampled months (33% of the time). The
lowest concentrations of dissolved oxygen at HAM were 1.4 mg/L, found in July
2002. The dissolved oxygen concentrations for Hammonds Creek are
represented graphically in Figure 3.3.1.
All sites within this subbasin were found to have a good
quality rating for chlorophyll a concentrations.
The North Carolina State Standard for chlorophyll a of 40 mg/L
was not exceeded at HAM, BRN, or NC11 during the 2002-2003 monitoring period.
Fecal coliform bacteria concentrations were low at NC11,
receiving a good quality rating with no samples over the NC State Standard for
human contact waters of 200 CFU/100mL in 2002-2003.
Browns Creek (BRN) received a fair quality rating for fecal coliform
bacteria concentrations, exceeding the standard 25% of the time.
Hammonds Creek (HAM) was rated as poor quality for fecal coliform
bacteria concentrations, due to exceeding the NC State Standard in 33% of
samples. Fecal coliform bacteria
concentrations were greater than 4,000 CFU/100mL in March 2003 at HAM.
Also there were elevated turbidity concentrations noted during March
sampling, reaching 125 NTU at HAM. There
was heavy rain previous to and during the March Cape Fear River sampling, and
high water with flooded banks was noted at all sites within this subbasin. Fecal coliform bacteria concentrations for Browns Creek and
Hammonds Creek are represented graphically in Figure 3.3.2.
Though there were
elevated turbidity levels noted in the March 2003 sampling, all sites within
this subbasin were rated as good quality for turbidity concentrations.
The March 2003 samples were the only ones to exceed the 50 NTU North
Carolina State Standard for turbidity. The
concentrations for March 2003 were 85 NTU, 125 NTU, and 86 NTU for BRN, HAM, and
NC11 respectively. The means for
the 2002-2003 sampling period were 12 NTU (BRN), 17 NTU (HAM) and 27 NTU (NC11).
Figure 3.3.1
Dissolved oxygen concentrations (mg/L) for Hammonds Creek (HAM).
The line shows the NC State Standard of 5.0 mg/L.
Figure 3.3.2.
Fecal coliform bacteria concentrations (CFU/100mL) for Browns
Creek (BRN)
and Hammonds Creek (HAM). The line
shows the NC State
Standard for human contact waters of 200 CFU/100mL.