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FATE OF MERCURY IN THE ARCTIC Michael Evan ... - COGCI

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Fate of Mercury in the Arctic 102<br />

RGM pg m-3<br />

500<br />

450<br />

run nr. 2, valve stuck open in REA<br />

system<br />

400<br />

350<br />

300<br />

250<br />

200<br />

150<br />

100<br />

50<br />

0<br />

Comparison of total RGM concentrations, Barrow 2001<br />

1130 total<br />

RGM REA total<br />

1 2 3 4 5 6 7 8 9 10 12 11(dark)<br />

REA flux run number<br />

Figure 22 A comparison of RGM air concentrations between the REA system and a co-located TEKRAN model<br />

1130 mercury speciation unit. Due to the different heating mantles, it is expected that the REA<br />

system will have lower RGM values, since the annular denuders were only heated to 50 0 C above<br />

ambient. and did so in all but 2 cases, excluding run nr. 2. The average percent difference between<br />

the two measurements is 24% with a standard deviation of 42, excluding run nr. 2. RGM<br />

measurements from S. Brooks TEKRAN 1130, this author used a linear relationship between time<br />

and concentration for the 2537A since the run start times for the two instruments were different.<br />

The flux was divided by the total concentration to determine the depositional velocity. Table 2.<br />

page 75, has the average values reported in the REA system data output file runname.txt. It is seen<br />

that for the measurement periods, the average temperature was rising, during the campaign, while<br />

wind speed was on average, generally consistent. Wind direction was more variable coming from<br />

the direction of Barrow most of the time, instead of the coast. The standard deviation of the vertical<br />

wind velocity and the value for the proportionality constant, are on average, stable, as should be<br />

expected for the weather conditions.

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