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GCI
TECH NOTES©
Volume
16, Number 2
A Gossman
Consulting, Inc.
Publication
February 2011
BACT for GHG (Green House
Gas) from Cement
Plants
– A Critical Error
in the EPA BACT
Example
by
David Gossman
Introduction
EPA
recently released a series of
videos of slide presentations on Best Available Control Technology
(BACT)
analysis for GHG for various industries. One of the BACT analysis
examples
provided is for a cement plant. There are significant errors in this
analysis
that would likely negatively impact GHG emissions and provide a further
barrier
to modernization and construction of new cement plants in the US.
Issues
EPA’s
BACT analysis example
contains many of the basic components that one might expect. These
include
alternative fuel options, modern design, maintenance, computer control
and an
analysis of the potential for sequestration. Most of these have
expected and
logical outcomes based on the currently available technology. There are
two
issues that are raised with potential errors in the analysis that are
likely to
have the opposite-to-intended effect. One of these is relatively minor,
the
other is major.
The
minor
issue is that of
location. The example cement plant is assumed to be providing cement in
a local
market, that is with minimal transportation GHG emissions.
While this seems reasonable
on the surface,
recent changes to EPA MACT requirements for cement plants are likely to
move
some new cement plants to locations quite distant from their markets to
either
obtain raw materials that will allow cement plants to meet the new MACT
emission restrictions or to move the plant outside of the US altogether
to
avoid these restrictions. Either moving a plant to a location with
“cleaner”
raw materials or out of the country will have potentially large
negative
impacts on GHG emissions.
The
second
issue is large and
troubling in nature. EPA, in this BACT example for a cement plant,
proposes to
require the plant to produce a blended cement via the substitution of
at least
5% fly ash in the finished product.
Analysis
For
those
not familiar with the
cement industry, the requirement for blended cement might appear
logical and
desirable. Quite the opposite is the case. It has to be understood that
Portland cement is manufactured to exacting standards set down by ASTM.
ASTM
standards are required to be honored during the process of developing
and
enforcing EPA regulations by virtue of well established government
policy,
directives and legislation. To put it simply, cement that has 5% or
more fly
ash is no longer Portland cement but is instead a blended cement, both
being
clearly defined terms by ASTM. EPA is literally requiring the plant to
manufacture a different product as part of this BACT analysis,
something that
is clearly prohibited by the Clean Air Act.
Further,
blended cements shipped
from cement plants in most areas of the US simply do not exist. For
example,
there were a total of 2,158 metric tons of blended cement shipped in
Illinois
during October 2010 compared with 294,221 metric tons of Portland
cement. No
blended cement was shipped in the Chicago market during this same time
period.
Blending of fly ash and other materials after the manufacture of
Portland
cement is done at the end-use sites, that is, at ready-mix plants. At
those
sites these types of blends can vary from 0% substitution to 50% or
more substitution
depending on the end-use specifications, which are quite often set by
other
government agencies. If these ready-mix plants were required to accept
a
preblended cement from cement plants it would severely restrict their
ability
to meet market requirements and restrict their ability to blend cements
mixtures that maximize the use of byproducts such as fly ash and also
minimize
overall GHG emissions.
In
most
cases the maximizing of
the use of blended cements is also a matter of scale. Smaller ready-mix
plants
are in a far better position to blend the relatively small batches of
finished
product and maximize the use of alternative cementitious materials than
the
much larger cement plant. Even under a theoretical best case analysis
EPA has
done nothing in this BACT analysis to reduce GHG emissions –
they
have just
shifted the facility at which that activity is already accomplished.
Conclusion
Any
cement
company faced with the
alternative of making a product for which there is no market vs. moving
production
outside of the country is far more likely to choose the latter than the
former.
The net result is the loss of American jobs and increased emissions of
GHG.
If
the
example GHG BACT analysis
for cement plants provided by EPA is a typical example then there may
be
significant errors in other analyses in other sections of these EPA
video/presentations.
EPA’s
attempt to use the Clean
Air Act to control GHG emissions could have the opposite-to-the
intended
effect. By looking at specific facilities and point sources it is quite
likely
that EPA requirements will push GHG emissions off-site or even out of
the
country; with the added impact of actually increasing GHG emissions.
Clearly,
that is the case in the example given and, because of the unsuitability
of the
Clean Air Act as a mechanism for controlling GHG emissions, is likely
to
continue into the future so long as EPA pursues this approach.