3.11  Summary of all Stations  

Table 3.11.1  Use support ratings given by UNCW researchers for the LCFRP stations
for 2001-2002 sampling period for dissolved oxygen, chlorophyll a, fecal coliform
bacteria, turbidity and excessive nutrients, based in part on State Standards.

FS (fully supporting) – standard exceeded in < 10 % of the measurements
PS (partially supporting) – standard exceeded in 11-25 % of the measurements
NS (non supporting) – state standard exceed in > 25 % of the measurements

Subbasin

Station

DO

Swamp DO

Chl a

Fecal Coliform

Turbidity

Excessive Nutrients

03-06-16

BRN

FS

 

FS

FS

FS

 

 

HAM

PS (25%)

 

FS

PS (17%)

FS

 

 

NC11

FS

 

FS

FS

FS

 

03-06-17

LVC

FS

 

FS

FS

FS

 

 

AC

FS

 

FS

FS

FS

 

 

DP

FS

 

FS

FS

FS

 

 

IC

PS (25%)

 

FS

FS

FS

 

 

NAV

NS (33%)

 

FS

FS

FS

 

 

HB

FS

 

FS

PS (25%)

FS

 

 

BRR

FS

 

FS

FS

PS (17%)

 

 

M61

FS

 

FS

FS

FS

 

 

M54

FS

 

FS

FS

PS (17%)

 

 

M42

FS

 

FS

FS

FS

 

 

M35

FS

 

FS

FS

FS

 

 

M23

FS

 

FS

FS

FS

 

 

M18

FS

 

FS

FS

FS

 

 

SPD

FS

 

FS

FS

FS

 

03-06-18

SR

NS (50%)

NS (42%)

FS

PS (25%)

FS

 

03-06-19

LCO

FS

 

FS

FS

FS

 

 

GCO

NS (33%)

PS (17%)

FS

FS

FS

 

 

6RC

FS

 

FS

PS (17%)

FS

 

03-06-20

COL

FS

 

FS

FS

FS

 

 

B210

FS

 

FS

FS

FS

 

 

BBT

PS (17%)

 

FS

no sample

FS

 

03-06-21

N403

NS (66%)

NS (58%)

FS

FS

FS

TP and nitrate-N

03-06-22

PB

NS

NS (33%)

FS

FS

FS

TP and nitrate-N

 

GS

NS

NS (33%)

PS (17%)

PS (17%)

FS

 

 

SAR

FS

 

FS

FS

FS

 

 

LRC

FS

 

NS (50%)

NS (50%)

FS

 

 

ROC

FS

 

FS

FS

FS

TP and nitrate-N

03-06-23

ANC

NS (58%)

NS (58%)

FS

PS (17%)

FS

TP and nitrate-N

 

BCRR

NS (50%)

NS (50%)

PS (17%)

NS (50%)

FS

 

 

BC117

FS

 

FS

NS (67%)

FS

TP and nitrate-N

 

NCF117

PS (25%)

PS (17%)

FS

FS

FS

 

 

NCF6

FS

 

FS

FS

FS

 

        Of the 35 stations monitored by the Lower Cape Fear River Program, twelve sites had low dissolved oxygen levels.  66% of the stations were fully supporting for dissolved oxygen.  Nine stations had excessive fecal coliform bacteria concentrations, and 75% of stations were found to be fully supporting.  Two stations were partially supporting for turbidity concentrations, and 94% of sites were found to be fully supporting.  One station was found to be partially supporting for chlorophyll a concentrations and 97% of stations were fully supporting.  Five stations were identified as having excessive nutrient levels.  High total phosphorus levels and high nitrate-nitrite levels were detected in 14% of stations.

           

3.12   Acknowledgment

We thank Melissa Smith of the UNC Wilmington CMS for much help in producing the graphics for this chapter.

 

3.13    References Cited

Mallin, M.A., M.H. Posey, G.C. Shank, M.R. McIver, S.H. Ensign and T.D. Alphin. 1999. Hurricane effects on water quality and benthos in the Cape Fear Watershed: Natural and anthropogenic impacts. Ecological Applications 9:350-362.

Mallin, M.A., L.B. Cahoon, D.C. Parsons and S.H. Ensign. 2001. Effect of nitrogen and phosphorus loading on plankton in Coastal Plain blackwater streams. Journal of Freshwater Ecology 16:455-466.

Mallin, M.A., L.B. Cahoon, M.R. McIver and S.H. Ensign. 2002. Seeking science-based nutrient standards for coastal  
     blackwater stream systems.  Report No. 341. Water Resources Research Institute of the University of North Carolina, 
     Raleigh, N.C.

NCDENR. 2000. Cape Fear River Basinwide Water Quality Plan. North Carolina Department of Environment and Natural Resources, Division of Water Quality, Water Quality Section, Raleigh, NC, 27699-1617.