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NEW: Annual Report - George Mason University

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density of clupeids and Morone sp. occurred in late May, while yellow perch peaked in<br />

early April.<br />

White perch was the most common fish collected in trawls comprising 30% of the total.<br />

Blueback herring (23.2%), channel cat (9.8%), and bay anchovy (9.1%) rounded out the<br />

group of most common species. In an unusual reversal, blueback herring were actually<br />

more common than white perch at both cove trawl sites. Most of the blueback herring<br />

were collected on three sample dates while the white perch were more evenly distributed<br />

through the year.<br />

Banded killifish was the most common species collected at seine sites comprising 44% of<br />

the total catch. Other common species were bay anchovy (12.4%), white perch (6.9%),<br />

and spottail shiner (6.8%). Banded killifish were the most abundant species at all seining<br />

sites and on most sampling dates.<br />

State and federal scientists have collected adult snakeheads this spring in Gunston Cove<br />

at our Station 6 seine site using electrofishing boats and much longer seines. The<br />

smallest was about 5-8 inches longs, but they also caught a large female that seemed<br />

ready to spawn. They asked us to notify them if we get any juveniles or adults. We feel<br />

confident that we can identify them.<br />

Oligochaetes were the most abundant macrobenthic organisms in 2003 with similar<br />

densities observed in both river and cove. Chronomids were a close second in the cove<br />

while amphipods (scuds) and the Asiatic clam Corbicula were subdominant in the river.<br />

Isopods, spherid clams, and gastropods were also present in the river. Small populations<br />

of gastropods and chaoborids (phantom midges) were found in the cove.<br />

B. Water Quality Trends: 1983-2003<br />

To assess long-term trends in water quality, data form 1983 to 2002 were pooled into a<br />

single data file. The, subgroups were selected based on season and station. For water<br />

quality parameters, we focused on summer (June-September) data as this is the most<br />

stable period and often presents the greatest water quality challenges and the highest<br />

biological activity and abundances. We examined the cove and river separately with the<br />

cove represented by Station 7 and the river by Station 9. We tried several methods for<br />

tracking long-term trends, settling on a scatterplot with LOWESS trend line. Each<br />

observation in a particular year is plotted as an open circle on the scatterplot. The<br />

LOWESS (locally weighted sum of squares) line is drawn by a series of linear<br />

regressions moving through the years. The allows the detection of nonlinear patterns such<br />

as cycles and lags which are not easily detected by linear approaches such as linear<br />

regression. We also calculated the Pearson correlation coefficient and performed linear<br />

regression to test for statistical significance of a linear relationship over the entire period<br />

of record (Tables 10 and 11). This was similar to the analysis performed in the 2000 and<br />

2001 reports.<br />

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