WATER QUALITY IN THE LOWER CAPE FEAR RIVER SYSTEM, 1995-1996
by
Michael A. Mallin, G. Christopher Shank, Matthew R.
McIver
and James F. Merritt
Under the auspices of the Cape Fear River Program a broad-scale
water sampling program in the Cape Fear watershed was begun in June 1995. Sixteen stations
throughout the estuary and the lower Cape Fear, Black, and Northeast Cape Fear Rivers were
sampled monthly, with the number of stations increased to 34 in February 1996. Data were
collected for a variety of physical, chemical, and biological parameters.
The mainstem Cape Fear River was characterized by high inorganic
nutrient concentrations, moderate chlorophyll a biomass, high turbidity levels, and
summer-early fall substandard dissolved oxygen levels. The main blackwater tributaries
(the Black and Northeast Cape Fear Rivers) have much lower inorganic nutrient
concentrations, low chlorophyll a biomass, very low turbidity levels, and low
summer-fall dissolved oxygen levels. These blackwater rivers also differ from the mainstem
Cape Fear in that most of the nitrogen and phosphorus (particularly nitrogen) is in the
non-biologically available organic form rather than the inorganic species (nitrate,
ammonia, orthophosphate). The extensive riverine wetlands bordering these blackwater
systems appear to serve as efficient pollutant filters.
The Cape Fear Estuary was characterized by moderate to high nutrient
concentrations, moderate to high chlorophyll a biomass, periodic pulses of high
turbidity, and summer-fall low dissolved oxygen in the upper estuary. The higher
chlorophyll a concentrations (up to 29 ug/L) were found in the mid-to-lower
estuary during the summer months. The high turbidity pulses were caused by non-point
source runoff in the mainstem Cape Fear River watershed, and also from periodic dredging
activities in the estuary. Causes of the river-upper estuary dissolved oxygen sag appear
to be a combination of BOD loading from the pulp and paper industry along the mainstem
Cape Fear River and contributions from oxygen-poor swamp waters draining into the
blackwater tributaries.
Vertical profiles and surface and bottom sampling results indicated
that the riverine water column was well-mixed. There were no significant overall physical
differences and few significant chlorophyll or nutrient differences (less than 20% of the
time) between surface and bottom. The estuarine water column was likewise usually
well-mixed, with occasional elevated salinity and turbidity near the bottom in
mid-estuary. Chlorophyll and nitrogen concentrations showed no consistent vertical
differences in the estuarine water column. Total phosphorus and ammonia showed periodic
higher bottom-water concentrations (TP 34% of the time and ammonia 27% of the time). The
well-mixed nature of the river and upper estuary prevented the formation of anoxic bottom
waters. However, this same phenomenon also cause low dissolved oxygen levels (2-5 mg/L) to
be maintained in the surface as well as bottom waters.
Several animal waste lagoon spills occurrd in the Cape Fear watershed
during summer 1995. We extensively sampled two of these, a 8.5 million gallon poultry
lagoon rupture in the Northeast Cape Fear watershed in Duplin County and a two million
gallon swine waste lagon leak near Town Creek in Brunswick County. The spills caused high
nutrient loads to enter receiving waters (particulary amminia and orthophosphate), algal
blooms, fish kills, and high turbidity concentrations. The BOD introduced by the spills
caused low dissolved oxygen problems in local receiving streams and a dissolved oxygen sag
in the Northeast Cape Fear River that registered its lowest reading 55 miles downstream of
the waste input into the river. Elevated nutrients from the spill were also found at this
downstream location. The spills also introduced high concentratins of fecal coliform
bacteria and other pathogens to the receiving waters. The potential of environmental
damage from the growing number of waste lagoons in the watershed is considerable,
partcularly under adverse weather conditions (noreasters, tropical storms or
hurricanes).
| 1.0 Introduction 1 Site Description |
2.0 Physical, Chemical
and Biological Parameters 1 Introduction 2 Materials and Methods 3 Results and Discussion 4 Preliminary Results from New Sites Data Tables of Results |
3.0 Vertical
Distribution of Water Quality Parameters 1 Introduction 2 Methods 3 Results 4 Discussion |
| 4.0 Effect of Animal
Waste Spills in the Cape Fear Watershed 1 Introduction 2 Physical Effects 3 Chemical Effects 4 Biological Effects 5 Conclusions |
5.0 References Cited | 6.0 Acknowledgments |
**Any tables or figures not included on this site are available in hard copy from the Center for Marine Science at the University of North Carolina at Wilmington**