
Air Quality Laboratory Begins Regional Study
Measurement: Particulate-phase Mercury
Method Description *:
Open-face Teflon filter pack with glass fiber filter
Extracted in 10% HNO3 with microwave digestion
Analyzed by cold-vapor atomic fluorescence
spectroscopy (CVAFS)
Measurement: Gas-phase Mercury
Method Description:
Gold-coated glass bead traps analyzed by CVAFS
Measurement: Particulate Trace Metals
Method Description:
Open-face Teflon filter pack with Teflon filter
Analyzed by XRF at US EPA-NERL
UMAQL methods to be published in the US-EPA Compendium of Methods For Toxic Pollutants, 1996.
Great Lakes Agencies Meet at UMAQL WorkshopRepresentatives from federal, state and provincial agencies for the Great Lakes region met with scientists studying atmospheric mercury at a workshop held at the University of Michigan on July 7th and 8th, 1994. The goals of this workshop were to:
-finalize the monitoring program to assess atmospheric mercury levels in the Great Lakes region (i.e. sampling site locations),
-provide an overview of state-of-the-art mercury sampling and analysis techniques and ongoing mercury measurements in the region,
-describe the plan for determining the major source areas for atmospheric mercury in the Great Lakes region,
-identify common goals withother programs and potential for collaboration.
The UMAQL sponsored the workshop to promote cooperation among the Great Lakes agencies that would be needed to establish the regional monitoring network. Involving these groups in the design of the monitoring activities proved to be an important step in generating support for the project.
Monitoring Sites EstablishedThe UMAQL has established more than ten sites for the GLAMAP monitoring network. These include the five Integrated Atmospheric Deposition Network (IADN) master sites along the Great Lakes shores. The other sampling locations were chosen by the workshop participants to complete the spatial coverage of the Great Lakes region. Selected sites were required to be in rural or remote areas in order to investigate the regional transport of atmospheric mercury. The locations of the GLAMAP sites within the Great Lakes region are displayed in Figure 1.

UMAQL staff began installation of the sampling equipment and operator training
for GLAMAP in November 1994. The sampling equipment includes a fiberglass box mounted
to the top of a three meter pole. Inlets to the sample filter packs protrude from the
bottom of the box during sampling. Hard-walled polyethylene tubing connects the sampling
box to the pump unit, which consists of three separate pumps and an internal heater. The
unit is enclosed in an insulated wooden box for protection during harsh winter conditions
encountered at several of the sites.
After the equipment was installed and tested, site operators were trained in the proper
techniques for handling and collecting atmospheric mercury samples. Many of the operators
had collected samples for other research projects and already had experience with standard
operating procedures for air pollution studies.


Since December 1992, the UMAQL has been conducting atmospheric mercury sampling near Lake Champlain at the Proctor Maple Research Center in Underhill Center, VT. Tim Scherbatskoy of the University of Vermont and the Vermont Monitoring Cooperative supervises the mercury monitoring at this site. Joanne Cummings collects the samples with help from Mim Pendleton.
Three additional sites in the southern Lake Michigan basin were operational through October 1995 as part of the Lake Michigan Mass Balance Study. Two of the sites were located in rural areas near the lake shore: Kenosha, WI and South Haven, MI. The third site was located in downtown Chicago, IL.
Regional Database GeneratedThe measurements of atmospheric mercury and trace metals for the GLAMAP multi-site network will generate a significant amount of data over the two years of the study.
Analysis and interpretation of this large data base will provide the first spatially resolved assessment of atmospheric mercury levels for the entire Great Lakes region. Seasonal variation in atmospheric mercury concentrations, as well as year-to-year variation, will be evaluated based on the two years of measurements.
Air mass trajectories for each site will be used to investigate the transport of this contaminant across theregion. Hybrid receptor modeling techniques will combine the air mass trajectories with the levels of atmospheric mercury to quantify the relative impact of different source areas for the Great Lakes region.
Trace metal levels will be used in source apportionment techniques to explore the relationship between different source types and atmospheric mercury levels in the Great Lakes region.
In addition, the GLAMAP results could be used in the refinement of computer models simulating the transport and deposition of mercury in the Great Lakes region.
Preliminary Results Show Differences Within RegionThe following preliminary results from the GLAMAP monitoring network are presented to illustrate the site-to-site variation in ambient mercury concentrations that will become the basis for identifying source areas for this contaminant in the Great Lakes region. Emphasis here is on vapor-phase mercury levels, since several months of data are currentlyavailable for all of the sites. These data are preliminary and requests for final results should be directed to Gerald Keeler at the UMAQL.

Sites located within the eastern and southern Great Lakes region tend to have higher average concentrations than sites in the western and northern parts of the region. When an entire year of concurrent measurements is available for all the sites it will be determined whether the average vapor-phase mercury concentrations are statistically different across the Great Lakes region.
Variability in vapor-phase mercury levels at each of the monitoring locations is more pronounced at the eastern and southern Great Lakes sites where the maximum concentrations were above 3.0 ng/m3 (Figure 3). Sites in the northern and western areas of the Great Lakes region tend to have stable vapor-phase mercuryconcentrations less than 2 ng/m3. It should be noted that the concentrations displayed in Figure 3 are for 24 hour samples collected on an every sixth day schedule.

AcknowledgmentsGary Evans, Project Manager, US EPA-NERL; Jackie Bode of the US EPA Great Lakes National Program Office (GLNPO) for the United States IADN sites; Frank Fraude and Jim Owens of the Atmospheric Environment Service/Center for Atmospheric Research Experiments (AES/CARE) in Canada for the two Canadian IADN sites; Rick Strassman of the Minnesota Pollution Control Agency; Phil Downey of the Ohio EPA; Doug Knauer, Mark Allen and Bruce Rodger of the Wisconsin DNR; Marty Auer and James Pauer at Michigan Technological University; Kim Irvine at Buffalo State College; Clyde Sweet and Donald Dolske at Illinois State Water Survey; Steve Yancho and Tom Van Zoeren at Sleeping Bear Dunes National Lakeshore.
In ClosingAtmospheric Mercury in the Great Lakes Region will be published over the next two years to disseminate the key findings of the project. This first issue focuses on progress to date including the workshop in July 1994, descriptions of the monitoring locations, and the various agencies involved. Preliminary summaries of data available to date are also presented.
Future Issues
Plans for future issues include an analysis of the spatial and seasonal variation
of atmospheric mercury concentrations in the Great Lakes region using the first year
of results, followed by an assessment of the regional transport and source areas for
the atmospheric mercury.
Send comments or requests for copies of the newsletter to:
Gerald Keeler, Director
Univ. of Michigan Air Quality Lab.
Dept. of Environ. and Ind. Health
School of Public Health
109 S. Observatory
Ann Arbor, MI 48109-2029.
e-mail: jkeeler@umich.edu
Editor: Janet Burke
Production Coordinator:Anne Heybey
Copyright 1996, Ann Arbor, MI.