Abstract

Abstract. Long-term continuous measurements of gaseous elemental mercury (Hg0), reactive gaseous mercury (RGM), and particulate phase mercury (HgP) were conducted at coastal (Thompson Farm, denoted as TF), marine (Appledore Island, denoted as AI), and elevated inland rural (Pac Monadnock, denoted as PM) monitoring sites of the AIRMAP Observing Network. Diurnal, seasonal, annual, and interannual variability in Hg0, RGM, and HgP from the three distinctly different environments were characterized and compared in Part 1. Here in Part 2 relationships between speciated mercury (i.e., Hg0, RGM, and HgP) and climate variables (e.g., temperature, wind speed, humidity, solar radiation, and precipitation) were examined. The best point-to-point correlations were found between Hg0 and temperature in summer at TF and spring at PM, but there was no similar correlation at AI. Subsets of data demonstrated regional impacts of episodic dynamic processes such as strong cyclonic systems on ambient levels of Hg0 at all three sites, possibly through enhanced oceanic evasion of Hg0. A tendency of higher levels of RGM and HgP was identified in spring and summer under sunny conditions in all environments. Specifically, the 10th, 25th, median, 75th, and 90th percentile mixing ratios of RGM and HgP increased with stronger solar radiation at both the coastal and marine sites. These metrics decreased with increasing wind speed at AI indicating enhanced loss of RGM and HgP through deposition. RGM and HgP levels correlated with temperature positively in spring, summer and fall at the coastal and marine locations. At the coastal site relationships between RGM and relative humidity suggested a clear decreasing tendency in all metrics from <40% to 100% relative humidity in all seasons especially in spring, compared to less variability in the marine environment. The effect of precipitation on RGM at coastal and marine locations was similar. At the coastal site, RGM levels were a factor of 3–4 to two orders of magnitude higher under dry conditions than rainy conditions in all seasons. In winter RGM mixing ratios appeared to be mostly above the limit of detection (LOD) during snowfalls suggesting less scavenging efficiency of snow. Mixing ratios of HgP at the coastal and marine sites remained above the LOD under rainy conditions. Precipitation had negligible impact on the magnitude and pattern of diurnal variation of HgP in all seasons in the marine environment.

Highlights

  • Mercury is a dangerous toxin detrimental to human health and it is of paramount importance to understand the processes that control the ambient levels of atmospheric mercury

  • We found that one-to-one corresponding relationships between speciated mercury and physical parameters of high temporal resolution were too scattered to yield meaningful correlations except Hg0 vs. temperature at TF and PM during the warm season

  • We present a comprehensive analysis of relationships that Hg0, reactive gaseous mercury (RGM), and HgP bore with climate variables in inland elevated rural, coastal, and marine environments using 3–7 yr of continuous data sets of high temporal resolution

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Summary

Introduction

Mercury is a dangerous toxin detrimental to human health and it is of paramount importance to understand the processes that control the ambient levels of atmospheric mercury. A ten month data set at Elora, Ontario, Canada suggested highest Hg0 concentrations in late spring and fall possibly due to increases in air temperature among other factors in spring and lower atmospheric mixing height in fall (Baya and Van Heyst, 2010) This relationship was supported by our study (Sigler et al, 2009a) with significant positive correlation between seasonally averaged Hg0 and temperature in spring and fall 2007 at a coastal and marine site from southern New Hampshire. There are limited long-term data sets of HgP, and their relationships with physical variables suggested that high levels were mostly associated with wind driven transport, chemical and physical transformation processes. In Part 3, we will further understand the key findings from Parts 1 and 2 using potential relationships between speciated mercury and other trace gases

Measurements and approach
Solar radiation
Temperature
Relative humidity
Precipitation
Discussion
Findings
Summary
Full Text
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