ILLINOIS POLLUTION CONTROL BOARD
August
7,
1981
IN THE MATTER OF:
AMENDMENTS TO CHAPTER
2, AIR
)
R79-11
POLLUTION CONTROL RULES AND
REGULATIONS, RULE 203(g).
PROPOSED OPINION OF THE BOARD
(by
I.
Goodman):
This Opinion supports the Order entered herein on ~July23,
1981.
On February 15,
1980,
Caterpillar Tractor Co.
(Caterpillar)
filed a substitute proposal to add a subsection to Rule 203(g) of
Chapter
2:
Air Pollution Control Rules and Regulations to
limit:
particulate matter
(TSP)
emissions from coal—fired industrial
boilers equipped with flue gas desulfurization systems
(scrubbers)
to 0.25 pounds of TSP per million Btu of actual heat input.
Although the original proposal submitted on September 5,
1979
limited the rule to spreader stoker boilers, Caterpillar’s
February 15,
1980 amended proposal proposed the rule’s appli-
cability to all industrial boilers using coal to provide energy
for heating, ventilation, manufacturing and related operations.
Technological hearings were held on January 16,
1980
in
Peoria and February 15,
1980 in Chicago; economic hearings were
held on January 13,
1981 in Chicago and January 19,
1981 in Peoria.
At hearings, testimony from Caterpillar and from both industrial
and environmental organizations was heard.
The
Board has received public comments from a business
organization, a governmental department, an environment~alorgan-
ization, and a legislator.
A newspaper article and a witness’
post—hearing responses to questions were also included in the
Board’s public comment file,
A synopsis of the written comments
follows.
The Illinois Department
of
Commerce and Community Affairs
supported the petition, citing Caterpillar’s history of commitment
to using available technology, the need to encourage industries to
use Illinois’ high sulfur—content coal,
and the need to adopt
environmental standards which are similar to those of adjacent
states in order to facilitate the Department’s efforts to retain
The Board acknowledges the assistance of Ms.
Terry
E. Cox
in the drafting of this Opinion and in acting as hearing officer
herein.
4~—147
—2—
existing Illinois industries.
United States Representative
Tom Railsback stated general support for the use of scrubbers
which enable the use of Illinois coal.
The Illinois Coal
Association
(ICA) stated that the greatest impediment to the
increased use of Illinois coal is the difficulty in reducing
sulfur dioxide emissions without the use of scrubbers,
which it
maintained are not yet fully developed control technologies.
The ICA further stated that retrofitting spreader stoker boilers
with scrubbers generates particulate matter, which side effect
should be weighed against the reduced sulfur dioxide emissions
gained with the use of scrubbers.
Finally,
ICA stated
that Cater-
pillar’s projected use by 1985 of 450,000 tons per year of Illinois
coal is not of insignificant consequence when presently some
17,000,000 tons of low sulfur,
non—Illinois coal are imported into
the state,
and that the use of oil
or gas would be an inefficient
use of energy resources.
Deere
& Company reiterated that the
effect of the proposal would be a reduction of Illinois Industry’s
dependence on foreign oil and thereby
a reduction of inflation.
Citizens For a Better Environment
(CBE) stated that the
proposal
should be restricted to boilers owned by Caterpillar
which are presently equipped with scrubbers,
and should not be
adopted as a statewide regulation.
CBE wrote that at the hearing
of January 13,
1981 the impact of the proposal upon ambient air
quality was not adequately assessed in that one affected source
had already installed a dry scrubber and other sources could be
ordered under various laws to convert to coal as
a fuel for
combustion.
Further,
CBE cites the fact that the Illinois
Institute of Natural Resource’s economic impact study considered
impact only with respect to four of Caterpillar’s five affected
Illinois plants.
Caterpillar’s petition states that of six Illinois industrial
sources constructing or using scrubbers on spreader stoker boilers,
five are Caterpillar’s plants.
Pending completed scrubber construc-
tion these five plants had controlled the particulate with multiclone
dry particulate dust (flyash)
systems.
Caterpillar intends to apply
to the United States Environmental Protection Agency
(USEPA) for a
new source, innovative system of continuous particulate matter
reduction determination pursuant to §111(j)
of the Clean Air Act
(CAA),
42 U.S.C.
§7401, et~.
(Petition, p.1,
ri 1.)
Caterpillar filed this proposal in conjunction with the
filing of four variance petitions
(PCB 79—188, —189, —190,
and
—191; see consolidated Order of November 29,
1979, modified
January 24, 1980,
and consolidated Opinion of November 29,
1979).
These variances from the particulates emission limitation of 0.10
lbs./million Btu
imposed, pending this regulatory proceeding,
limitations of 0.23 lbs./million Btu
(East Peoria boilers #21
1Contained in the State Implementation Plan (SIP)
(see §110(a)
of
the
CAA) as Rules 203(g)(1)(B)
and
(C).
See,
also,
Illinois
State Chamber of Commerce, et al. v. Illinois Pollution
Control
43f148
—3—
and #22), 0.27 lbs./million Btu (Mossville boiler
#5),
0.28 lbs.!
million Btu
(Joliet boiler #3), and 0.25 lbs./rnillion Etu for
thirteen other boilers at those four plants.
In those petitions,
Caterpillar alleged that its regenerative double alkali scrubbers
were an incompletely developed, innovative technology;
the Agency’s
variance recommendations concurred that these scrubbers had been
thought to be the best technology available when considered for
installation by Caterpillar during the early 1970’s.
Caterpillar’s
regulatory petition states that during hearings
in R71—23, which
first adopted Rule 203(g),
Zurn Industries,
Inc.,
a manufacturer
of the double alkali scrubbers, testified that the scrubbers would
reduce particulate emissions by 98,
hut that Caterpillar’s data
show only a 52—71
effectiveness.
Caterpillar states that its
problems are similar to those of General Motors Corporation.
(Petition, pp.14—15.)
Some of the excess particulate matter emissions are attribut-
able to the carryover of sulfuric acid mist and scrubber liquid
salts from the scrubbers.
Carryover contributions range from 18
(1977 Joliet stack tests)
to 50
(1979 Mossville stack tests).
USEPA has recognized this,
in relation to its particulates Test
Method25, as
a problem stemming from the combustion of high sulfur
coal.
Approxirnately half of the particulate emitted from
the
Joliet
and Morton boilers are greater than one micron in size; Caterpillar
has sought to reduce the amount of fine particulates
(submicron)
emitted,
and has identified some of its problems therewith.
For
example, when stored coal is exposed to natural elements, the
resulting increased moisture content causes variability in heat
output during combustion, and a boiler design criterion of 30
excess air can seldom be attained due to both the moisture content
and the lower ash fusion temperature.
Reinjection into the
boilers of flyash captured by the multiclones may cause increased
particulate emissions, and spreader stoker boiler manufacturers will
supply guarantees only as to combustion efficiency and not stack
emissions.
(Petition, pp.16—20).
Caterpillar alleges that its scrubbers are the best particulate
matter control technology available,
but that no technology exists
for satisfactory simultaneous control of both sulfur dioxide and
Board and consolidated cases,
67 Ill.App.3d 389,
384 N.E.2d 922
(1st Dist.1978), and People v. Commonwealth Edison Com~
and
related case, 490 F.Supp.
1145 (N.D.Ill.,1980).
The limitation
is also the one applicable as the new source performance standard
for industrial boilers.
Section 9.1(b) of the Illinois Environ-
mental Protection Act (Act);
40 C.F.R. §60.42.
2Public comment of Citizens For A Better Environment,
submitted during the First Notice period,
states that USEPA is
experimenting with a Test Method 5B at a General Motors plant
and is considering similar experimentation at one of Caterpillar’s
plants.
43—14!~
—4—
particulates when the combustion fuel
is Illinois coal.
Therefc~:e,
Caterpillar contends that it would be economically unreasonable for
the Board to require either additional controls or
the installation
of replacement technology.
The proposal, besides promoting the
combustion of Illinois coal,
and effectuating an economic boost
therefrom,
is alleged not to adversely impact ambient air quality,
although it is clear that more than twice the amount of particulate
allowed under the SIP and the new source performance standards
would be emitted into the atmosphere.
At hearings, evidence was received in support of Caterpillar’s
contentions.
When
the CAA and the Act were enacted in the
beginning of the 1970’s, Caterpillar experienced a variety of
problems with the combustion fuels of gas, oil, and low sulfur
coal
(R.16—21).
Although natural gas had been touted as being in
reasonable supply,
later federal regulations gave supply priority
to the public rather than to industry.
Caterpillar concluded that
natural gas was not a dependable fuel.
Oil similarly was unde-
pendable over the long tern~,primarily because producers had little
desulfurization capacity and because of ongoing federal regulatory
activity in the face of a continued unfavorable domestic—to—imported
ratio.
The use of electricity was considered to be prohibited by
cost.
As to low sulfur coal,
it was in short supply in the early
1970’s.
(Caterpillar defines “low sulfur” coal as coal for which
no scrubbers are necessary to meet sulfur dioxide emission
limitations.)
Caterpillar’s decision against low sulfur coal
centered upon the dependability of timely deliveries;
given
problems relating to rail transportation (labor,
car availability,
loading competition, accidents),
a steady supply was not foreseen.
In contrast,
Illinois coal could be transported by highway and
barge in addition to rail.
Caterpillar for these reasons decided
to use Illinois coal and to invest in the necessary scrubbers.
However, after this decision was made the supply of low sulfur coal
improved.
Caterpillar committed one of its plants to the use of
this coal
(R.19—20).
Several legal considerations involved in use of oil or natural
gas as combustion fuels exist.
The Powerplant and Industrial Fuel
Use Act of 1978, Pub.L.
95—620,
November
9,
1978,
92 Stat. 3289,
which supersedes the Energy Supply and Environmental Consideration
Act of 1974, prohibits the use of oil or gas in boilers upon which
construction commenced after November
9,
1978 unless an exemption
is obtained.
In addition, the United States Department of Energy
can require conversion to coal as the combustion fuel if boilers
have coal—burning capacity.
All of Caterpillar’s boilers have the
capacity to burn coal.
Finally, the Natural Gas Policy Act of 1978,
Pub.L.
95—621,
November
9,
1978,
92
Stat.
3350, had imposed mandatry
incremental pricing regimes on domestic natural gas supplies.
New source performance standards for industrial boilers (see
§111 of the CAA and 40 C.F.R.,
Part 60)
are expected to be proposed
by the USEPA in revised form in November of 1981.
In the alternative,
43—150
—5—
regulations may be promulgated which r~~ir~
utilizing adequately
demonstrated operational and other standards reflecting the best
technological
system of continuous emission reduction which takes
reduction costs as well as energy re.~uirerientsinto account
(~111(h)
of the CAA;
see also §111(a)(7) and
(8) and §111(b)(5) and
(6)).
Section 111(a) of the CAA would apparently give emission credit for
pre—combustion coal treatment (coal washing,
etc.), whereas such
credit is uncertain under §111(h).
Most of Caterpillar’s boilers
would be “new” sources for purposes of these provisions of the
CAA.
Nothing
in
this Order negates applicability of §111 of the
CAA.
Soon after the particulate matter emission limitations were
first promulgated by the Board,
Caterpillar determined that one way
to meet both the sulfur dioxide and the particulates emission
limitations would be to desulfurize the coal before applying control
equipment,3which procedure could address
the problem of small—sized
particles.
Such procedures would include coal heneficiation
(R.21—3).
The record contains no evidence as
to the technological
feasibility or economic reasonableness of these procedures.
On
October
27,
1978 Caterpillar met with representatives of the
Agency and of the USEPA to discuss improvements in scrubber tech-
nology.
The meeting was unsatisfactory.
Caterpillar’s experience
with venturi scrubbing has been unsuccessful, regardless of the
level of pressure drop during operation (R.76-8).
Caterpillar, then,
seeks a technology-based particulate matter
emission limitation;
the technology would be regenerative double
alkali scrubbers equipped with flyash arrestors
~
multiclonc
collectors) of good engineering practice design (R.25).
Some
measures to reduce or minimize the coal’s contribution to partic-
ulate emissions have been taken
(coal analyses upon delivery) but
some have not (storage in silos to prevent absorption of moisture)
(R.136—9)
Further support of an emission limitation greater than 0.10
lbs./million Btu was presented in a July,
1979 USEPA report of
pebble lime
(CaO)
or ground limestone
(CaCO3) scrubbers which
remove both sulfur dioxide and particulates without additional
particulate control equipment.
The report was based on 2—4
(medium—high) sulfur content coal and achieved emission rates
only as low as 0.15 lbs./million Btu, with typical rates ranging
from 0.20 to 0.30 lbs./million Btu.
Particulate removal averaged
93—4.
(See Ex.3.)
Caterpillar believes that its proposed 0.25—lb.
limitation for regenerative double alkali scrubbers is consistent
with this study
(R.50—1); however, the two control
systems are
not identical.
3USEPA is currently determining whether to regulate emissions
of particulates in terms of size; such regulations would likely
change the applicable particulate matter emission rates for both
new and existing sources.
See also 45 Fed.Re~.84098—9 regarding
Agency SIP submittals.
43—151
—6—
Caterpillar does not believe that ceasing the reinjection of
flyash, which can lower particulate emissions, would justify the
increased energy expenditures occasioned thereby.
To improve the
performance of its scrubbers, Caterpillar has improved the operation
of the demisters, modified its chemicals handling procedures,
and
replaced bypass dampers to minimize leakage.
To date,
$27 million
has been expended by Caterpillar to meet both sulfur dioxide and
particulate emission limitations
(R.39—1,117,126—8).
It alleges
that its present system constitutes “best available
particulate
matter
control technology”
(see §169(3) of the CAA)
and that it
would be technologically infeasible and economically unreasonable
to require, in order to meet both sulfur dioxide and particulates
emission limitations,
either additional controls or, assuming the
availability of a new generation of scrubbers or other technology,
replacement of its existing controls.
Caterpillar alleges that
the “ultimate solution” to compliance with both sulfur dioxide
and particulate emission limitations when using high sulfur coal
is the desulfurization of that coal in order to make the use of
scrubbers unnecessary and to enable the use of particulate matter
controls without “scrubber interference”.
Desulfurizing the coal
would address the problem,
and not the result (R.41-2,47).
Indeed,
Caterpillar is unsure of the proportions of its particulate emis-
sions constituting flyash,
sulfuric acid mist,
or both.
Although
intermittent control systems and fluidized bed processes could
he appropriate control technologies
(R.168), these are allegedly
insufficiently developed to date.
Further development of controls
may be delayed if designers are made to consider intermittent
rather than continuous control methodologies.
Caterpillar’s boilers would not be the only sources subject
to its proposal.
At least one other source, the Pfizer plant
in
East St. Louis, presently uses s~rubbers(R.52).
Other possible
affected sources exist
(R.151—6)
but the record does not reveal
their identity or location.
Caterpillar seeks to have the proposal
apply statewide to all industrial boiler sources.
Particulate
matter removal capability, however, may be unrelated to other
physical or chemical plant and equipment configurations
(R.52—8).
Caterpillar hired ETA Engineering,
Inc.
(ETA)
to model the
expected air quality impacts of increasing the particulate matter
emission limitation from 0.10 to 0,25 lbs,/million Btu.
Its
report was made Exhibit
6 to this proceeding.
(The Illinois
Institute of Natural Resource’s economic impact study,
see post,
which also evaluated air quality impacts, considered four of
4me Agency pointed out that Caterpillar’s proposal may force
Pfizer’s plant to decrease allowable emissions by 7.7 pounds per
hour from its three boilers which vent to one stack
(R.159—1).
Although the Illinois Manufacturers’ Association is conducting
a
survey to ascertain potentially affected sources
(R.155—6),
the
record does not contain the results of such study.
However, any
industrial
source having scrubbers comes within the rule.
43—152
—7—
Caterpillar’s plants,
whereas ETA’s considered the Morton plant
as
well.)
ETA’s study used as input to USEPA’s Climatological
Dispersion Model
(CDM) projected 1980 Illinois coal usage data
and current stack test data.
One hundred sixty-eight equidistant
receptors points were used; annual
concentrations were based on
“expected 1980 annual emission rates” and the receptor area
concentrations were calculated by ratioing the concentrations in
proportion to the change in emissions were a 0.25—lb. limitation
to be allowed at each plant (R.91-2).
Incremental impact on air
quality was shown by computing the differences between concentration
levels monitored at the receptors;
maximum an~ualconcentrations
were used to estimate by the Larsen procedure
maximum 24—hour
concentrations.
Results of ETA’s modeling showed maximum annual concen~ratioris
of the five facilities, in micrograms per cubic meter
(ug/m
),
as:
Joliet,
3.0; Mossville,
2.7;
East Peoria,
1.1; Mapleton and Morton,
0.6.
These concentrations range from 0.80
(Mapleton) to 4.0
(Joliet) of the primary annual particulate matter national ambient
air quality standard
(NAAQS), and from 0.8
(Mapleton) to 5.5
(Joliet)
of the 24-h~urNAAQS.
Annual inemental
concentrations
ranged from 0.2 ug/m
(Morton)
to 2.3 ug/m
(Joliet);
the “level
of significance,” as defined by USEPA for PSD purposes,
is
1 ug/~
Twenty—four—hour incr~mentalconcentrations ranged from 0.7 ug/m
(Morton) ~o 11.2 ug/m
(Joliet); the “level of significance” here
is
5 ug/m
.
Although the Mossville plant as well as the Joliet
plant violate both “levels of significance,” the Mossville plant’s
impacts were measured within a 0.17—square—mile area around the
facility and were completely within the plant property.
As to
the Joliet plant,
44
of the readings were within plant property
and the remainder were upon nonresidential land within a 0.22—
square—mile area around the plant.
These figures are likely to
be inaccurate given that the Hi—Volume sampler reference method
can produce deviations from true statistical values of
+
50
depending on air flow rate and whether particulate has clogged
the filter (R.96—100).
No information regarding particle size
was presented, although Caterpillar has such information for at
least the Joliet and Morton facilities.
(Pet., p.17).
Caterpillar cites that reductions
in background concentrations,
particularly in Peoria and Joliet, will soon be achieved by reduc-
tions
of industrial and nontraditional source emissions of fugitive
dust mandated by recently promulgated R78-1i.
The CDM, however,
did not account for the effects of terrain.
Caterpillar furthe~
notes that none of the areas where concentrations over 1.0 ug/m
5The Larsen procedure uses as one variable the data’s
standard geometrical deviation;
this input is
allegedly higher for
the Joliet portion of the modeling than the correlative input used
by the Agency in its study of Peoria area air quality.
The result
might be ETA’S overestimation of both high and low maximm
concentrations for the Joliet area (R.106—7).
43—153
—8—
(24—hour) were recorded are accessible to the public
(R.134—5).
The
Board notes that Edwards power plant is 7.4 kilometers,
and
Powerton is 5.4 kilometers,
away from the Mapleton plant, and
that Wallace is 1.1 kilometers away from the East Peoria plant.
Caterpillar suggests that impact on air quality would be negligi-
ble because the variation in monitored incremental concentrations
would likely be greater than the entire contribution from the
plant;
in other words, the plant’s contributions are within the
error range of the monitoring technique itself
(R.113—4).
Caterpillar has spent over $27 million in capital costs
in an
effort to comply with both sulfur dioxide and particulates emission
limitations.
Caterpillar estimates that in order
to comply with a
0.10—lb. particulate emission limitation it would have to undergo
extensive modifications of its plants to accommodate the instal-
lation of particulates—control.ing
baghouses; however, there may
be insufficient space both within and outside of the plants for
the installation of baghouses.
Another modification would be the
replacement of the stack gas systems and, possibly, the stacks.
These modifications would consequently necessitate a change
in
electrical service to the newer and larger induced draft fan
systems.
Finally, it would be important not
to interrupt
the
boilers’
steam service for manufacturing operations.
Such modifi—
cations could be made at a capital expenditure of $50—60 million
over a three— to five—year period
(R.120—1, 128-0).
The economic impact study of the Illinois Institute of Natural
Resources,
Doc. No.
80/24,
November,
1980, “The Economic Impact of
R79—11
to allow a Relaxation of
Rule
203(g)”
(EIS), used these
Caterpillar cost estimates in balancing the “benefits” of the
proposal.
(“Benefits” in economic impact studies are typically
defined as foregone source expenditures when the environmental
proposal
is to loosen a standard because there can be no health
benefits to increased pollution.)
The study mentioned that besides
Pfizer, one other coal—fired industrial boiler source may exist
and stated that the degree of economic impact of the regulation
depends on the number and size of affected sources.
(EIS, pp.2—i
to 2—4.)
The EIS described the benefits of this regulation as
eliminated air pollution control costs associated with meeting the
limitations contained in the SIP.
(EIS,
pp.1—4.)
Four accounting
scenarios were projected to describe secondary costs
(described as
“loss of benefits,” pp.1—4) and secondary benefits
(described as
loss of costs to Caterpillar consumers and suppliers).
These were:
(1) all of Caterpillar’s costs were passed on to its consumers,
sales figures remaining constant;
(2)
costs were passed on but
Caterpillar expensed its capital and operating costs;
(3) costs
were not passed on and Caterpillar expensed over two years’ time;
and
(4) cost amounts were allocated to production rather than air
pollution controls.
(EIS, pp.5—i to 5-7.)
The study’s conclusion,
in comparing costs with benefits, is that from inauguration of the
$50—60—million compliance plan,
given a two—year construction
43—154
—9—
period,
the state economy obtains a short—term economic stimulus,
and that this stimulus will be greater if all equipment
is pur-
chased from Illinois manufacturers,
e.g., $91 million instead of
$57 million
(EIS, pp.6—2.)
When total health and other social
costs from the increased pollution,
not to be greater than $400,000
(depending on the damage coefficients used),
are considered, the
study’s conclusion is that the cost to Caterpillar of disallowing
its proposal is far greater than the cost to the public of allowing
its proposal.
The Board does not limit its findings to Caterpillar’s four
plants and will apply the regulation to other sources and
installations.
The Board has adopted an Order with reference
to all sources existing as of the date of the final order herein
which presently have installed scrubbers of any kind.
However,
the Board notes that,
pursuant to §9.1(b)
of the Act, presently
existing industrial boilers equipped with scrubbers may become
subject to the USEPA’s new source performance standards when they
are promulgated.
See also Part IX of Chapter 2:
Air Pollution
Control Rules and Regulations.
Although conversion to coal from
another type of fuel alone may not convert an existing coal—
designed source to a modified source for purposes of the CAA (40
C.F.R. §60.14), other operational modifications can lead to
ti-is
consequence.
A particulate matter emission limitation on industrial boilers
of 0.25 lbs./million Btu is found to be technologically feasible
using either wet or dry flue gas desulfurizatiori systems
(scrubhers).
Caterpillar as an example has met close to this limitation to date,
using high sulfur—content coal, and with further sensible preventive
practices (for example,
dry storage, pretreatment, and proper equip-
ment operation)
all affected sources will be able to consistently
meet both this limitation and the SIP’s sulfur dioxide limitation,
The Board also finds that allowing this higher emission
limitation is economically reasonable.
Given Caterpillar’s past
scrubber expenditures, allocated both for particulate matter
and
sulfur dioxide control, and given the scrubbers’
successful removal
of sulfur dioxide, the Board finds that requiring compliance with
anything other than
a technology-based emission limitation for
simultaneous compliance with particulate matter and sulfur dioxide
limitations would be economically unreasonable.
Caterpillar has
retrofitted multiclones upon the scrubber operation;
to require
redesign based upon the present scrubber equipment would involve
extensive modifications of plant,
equipment, and operating
procedures.
I,
Christan L. Moffett,
Clerk of the Illinois Pollution
Control
Board, hereby certify that the above Opinion was adopted
on the
‘7~’
day of
,
1981 by a vote of
____
Christan
L. Mof~e~t,Clerk
Illinos Pollutio~(ControlBoard
43—155