The Bradley Creek watershed is of particular current interest as a principal location for Clean Water Trust Fund mitigation activities, including the purchase and renovation of Airlie Gardens by the County. This creek is one of the most polluted in New Hanover County, particularly by fecal coliform bacteria (Mallin et al. 2000b). Seven stations were sampled in the past year, both fresh and brackish (Fig. 3.1).
As with last year, turbidity was not a problem during 2002-2003 (Table
3.1). The standard of 25 NTU was
not exceeded during our brackish water sampling except with a
construction-related episode in July 2003 (198 NTU - Table 3.1).
There were only minor problems with low dissolved oxygen (hypoxia), with
BC-NB having DO of less than 5.0 mg/L on two occasions and BC-CA having
substandard dissolved oxygen conditions on three of 12 sampling occasions (Appendix
B).
Table 3.1
Parameter concentrations at Bradley Creek sampling stations, August
2002-July 2003
(BC-CA from August 2003 – September 2003).
Data as mean (SD) / range, fecal coliform bacteria
as geometric mean / range.
_____________________________________________________________________
Station
Salinity
Turbidity
Dissolved Oxygen Fecal coliforms
(ppt)
(NTU)
(mg/L)
(CFU/100 mL)
_____________________________________________________________________
BC-76
28.8 (7.0)
9 (15)
7.7 (2.2)
NA
9.0-34.2
2-55
5.0-11.0
BC-SB
12.5 (12.8)
25 (55)
7.4 (1.9)
NA
0.1-31.6
2-198
4.9-11.1
BC-SBU
0.1 (0.0)
6 (6)
7.2 (1.4)
NA
0.1-0.1
2-22
5.3-9.4
BC-NB
21.1 (11.6)
10 (9)
7.1 (2.2)
NA
0.2-32.8
2-35
3.9-10.2
BC-NBU
0.1 (0.0)
9 (10)
7.6 (1.1)
NA
0.1-0.2
3-40
6.1-9.3
BC-CR
0.1 (0.0)
4 (6)
7.6 (0.8)
NA
0.0-0.1
0-18
6.5-8.8
BC-CA
0.1 (0.0)
8 (4)
6.3 (2.1)
1093
0.1-0.2
3-13
4.4-10.6
155-13000
_____________________________________________________________________
Only BC-CA was
sampled for fecal coliform concentrations last year, with elevated counts
exceeding the State standard of 200 CFU/100 mL occurring during 9 of 11
collections for an 82% exceedence rate (Table 3.1).
We consider that station to have poor water quality in terms of fecal
coliform counts (Appendix B).
Nitrate concentrations were highest at stations BC-CR, BC-SBU (upper
south branch) and BC-NBU. Nitrate
increased considerably over the previous year (in some cases more than
doubling), possibly as a result of the drought breaking and increased streamflow
(and stormwater runoff). Ammonium
was also elevated at BC-CA, and low at other locations.
The highest orthophosphate levels were found at BC-CA, with relatively
low orthophosphate levels at the rest of the stations (Table
3.2). Bradley Creek did not host excessive algal blooms in
2002-2003, except for a few minor blooms at BC-CA (20-32
mg/L,
Table 3.2).
Table 3.2.
Nutrient and chlorophyll a data
at Bradley Creek sampling stations, August 2002-July 2003
(BC-CA from August 2003 – September 2003).
Data as mean (SD) / range, nutrients in mg/L,
chlorophyll a as mg/L.
_____________________________________________________________________
Station
Nitrate
Ammonium
Orthophosphate
Chlorophyll a
_____________________________________________________________________
BC-76
0.021
(0.032) 0.026
(0.024)
0.007 (0.007)
1.97 (1.6)
0.006-0.121
0.006-0.087
0.001-0.027
0.7-6.4
BC-SB
0.088 (0.058)
0.036 (0.023)
0.011 (0.013) 3.2
(2.3)
0.013-0.212
0.004-0.069
0.002-0.052
0.8-8.4
BC-SBU
0.186 (0.108)
NA
0.009 (0.011) 2.5
(2.9)
0.044-0.464
0.001-0.044
0.2-10.2
BC-NB
0.029 (0.033)
0.032 (0.031)
0.009 (0.010) 3.9
(5.4)
0.005-0.123
0.006-0.105
0.001-0.036
0.7-20.5
BC-NBU
0.116 (0.047)
NA
0.004 (0.007) 1.5
(2.7)
0.069-0.250
0.001-0.023
0.1-9.2
BC-CR
0.270 (0.060)
NA
0.005 (0.007) 1.8
(2.9)
0.150-0.372
0.001-0.027
0.2-9.0
BC-CA
0.090 (0.056)
0.125 (0.073)
0.021 (0.012) 10.6
(9.6)
0.016-0.170
0.020-0.270
0.0102-0.045
1.7-32.0
_____________________________________________________________________