United States
Environmental Protection
Agency
National Risk Management
Research Laboratory
Research Triangle Park, NC 27711
Research and Development
EPA/600/SR-95/106
August 1995
Project Summary
Effects  of Changing
Coals on  the  Emissions  of
Metal  Hazardous  Air
Pollutants from the
Combustion  of Pulverized
Coal
C. Andrew Miller
  Tests were conducted at the U.S. En-
vironmental  Protection Agency's Air
Pollution Prevention and Control Divi-
sion  (APPCD) in Research Triangle
Park, NC, to evaluate the  effects of
changing coals on  the emissions of
metal hazardous air pollutants from
coal-fired boilers. The objectives of the
tests were to determine how the emis-
sions of metal hazardous air pollutants
would change if low sulfur coals were
substituted for higher sulfur coals and
to measure  the correlation between
emissions from a small scale combus-
tor and emissions from a full scale util-
ity boiler burning the same coal. The
tests were funded by the Illinois Clean
Coal Institute.
  This Project Summary was developed
by EPA's National Risk Management
Research Laboratory's Air  Pollution
Prevention and Control  Division, Re-
search Triangle Park, NC, to announce
key findings  of the research project
that is fully documented in a separate
report of the same title (see Project
Report ordering information at back).

Overview
  The small scale tests were conducted
on APPCD's 29 kW (100,000 Btu/hr) In-
novative  Furnace Reactor (IFR), and
samples were taken prior to any pollution
control equipment to allow application of
different control efficiencies to the uncon-
trolled emissions. Six coals were burned
in the IFR under similar combustion con-
ditions, and each coal was sampled for 10
 metals: antimony, arsenic, beryllium, cad-
 mium, chromium, lead, manganese, mer-
 cury, nickel, and selenium. Each of these
 metals is on the list of 189 compounds
 and compound classes listed as hazard-
 ous air  pollutants under Title III of the
 1990 Clean Air Act Amendments. The six
 coals included two Illinois bituminous coals
 with an  average  sulfur content of 2.23%
 (the high sulfur coals in this test program),
 two western subbituminous coals with an
 average sulfur content of 0.57%, and two
 other coals used in full  scale test pro-
 grams. The final  two coals were chosen
 to allow a direct comparison of the small
 scale results to full scale emissions tests.
   No general correlation was found be-
 tween sulfur content and metals emissions
 for the six coals  tested. This result is in
 agreement with previous results that have
 noted no general  correlation between sul-
 fur content and  metal content in  coals.
 The small scale IFR emissions correlated
 well with emissions from a full scale utility
 boiler burning the same coal, although the
 IFR results tended to be consistently lower.
 The difference is likely due  to physical
 differences in the two systems, such as
 the volume to surface area ratio, and the
 sharpness of turns in the gas path.
   The results of the IFR tests showed
 that changes in  the uncontrolled emis-
 sions tended to  correlate well with the
 corresponding changes in the as-fed metal
 content  of the coals for arsenic, mercury,
 and selenium. For  beryllium, chromium,
 manganese,  and nickel,  changes  in the
 uncontrolled emissions with different coals
                                               Printed on Recycled Paper

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did not correlate well with the changes in
the as-fed trace metal contents. The re-
maining three metals, antimony, cadmium,
and lead, did not show conclusive results
when comparing emissions to as-fed trace
metal contents. The factor that determines
the degree of correlation between the as-
fed trace metal concentration and the un-
controlled stack emissions appears to be
the vapor pressure of the metal.  Metals
that have  high  vapor pressures tend to
exhibit strong correlations between the as-
fed metal  concentration  in the coal  and
the uncontrolled emissions,  while metals
with low vapor pressures  tend to show a
much  weaker correlation. In summary, the
study illustrates that predictions of metal
emissions based only on the trace metal
content of the coal are not accurate in all
cases. Such predictions cannot be used
with any confidence for refractory metals,
but do have some degree of validity for
the more volatile metals of interest.
 The EPA author, C. Andrew Miller (also the EPA Project Officer, see below) is with
   the National Risk Management Research Laboratory's Air Pollution Prevention
   and Control Division, Research Triangle Park, NC 27711.
 The complete report, entitled "Effects of Changing Coals on the Emissions of Metal
   Hazardous Air Pollutants from the Combustion of Pulverized Coal," (Order No.
   PB95-246385; Cost: $19.50, subject to change) will be available only from:
         National Technical Information Service
         5285 Port Royal Road
         Springfield, VA 22161
         Telephone: 703-487-4650
 The EPA Project Officer can be contacted at:
         Air Pollution Prevention and Control Division
         National Risk Management Research Laboratory
         U.S. Environmental Protection Agency
         Research Triangle Park, NC 27711
United States
Environmental Protection Agency
National Risk Management Research Laboratory (G-72)
Cincinnati, OH 45268

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