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NEW: Annual Report - George Mason University

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66<br />

Chloride (mg/L)<br />

350<br />

300<br />

250<br />

200<br />

150<br />

100<br />

50<br />

Station 7: June-Sept<br />

1980 1985 1990 1995 2000 2005<br />

YEAR<br />

Chloride levels were clustered<br />

in a narrow range just under<br />

50 mg/L for the entire study<br />

period (Figure 70). Higher<br />

values observed in some years<br />

were probably due to the<br />

estuarine water intrusions that<br />

occur in dry years. The trend<br />

line indicated a slight decline<br />

in recent years, but a linear<br />

regression demonstrated a<br />

significant linear increase in<br />

chloride over the study period<br />

at a rate of about 1 mg/L per<br />

year (Table 11).<br />

Figure 70. Long term trend in Chloride (NC Lab Data). Station 7. Gunston Cove.<br />

Chloride (mg/L)<br />

400<br />

300<br />

200<br />

100<br />

Station 9: June-Sept<br />

1980 1985 1990 1995 2000 2005<br />

YEAR<br />

Chloride in the river has been<br />

slightly more variable than in<br />

the cove (Figure 71). The<br />

higher readings are again due<br />

to brackish water intrusions in<br />

dry years. A slight trend of<br />

increasing values in the<br />

1980’s and decreases in the<br />

late 1990’s and 2000’s was<br />

suggested by the trend line.<br />

Regression analysis revealed<br />

a significant linear increase of<br />

about 1 mg/L per year (Table<br />

11).<br />

Figure 71. Long term trend in Chloride (NC Lab Data). Station 9. River mainstem.

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