ILLINOIS
 POLLUTION CONTROL BOARD
February
 24,
 1983
IN THE MATTER OF:
 )
CITY OE ROCHELLE:
 )
 R78-15
SITE SPECIFIC LIMITATION FOR
 )
TOTAL SUSPENDED PARTICULATE MATTER
 )
~jated
 Rule.
 Final Qpinion.
OPINION AND ORDER OF THE BOARD
 (by
 I.
 G.
 Goodman):
On November
 13,
 1978 the City of Rochelle (Rochelle)
 filed
a petition to amend Rule 203(g)(l)
 of Chapter
 2:
 Air Pollution
to include a particulate emission limitation for the emissions
exhausted from the stack at its Municipal Steam Power Plant,
located on South Main Street.
 Specifically, Rochelle requested
a limitation of 0.6 pounds per million British thermal units
(lhs/mBtu)
 of actual heat input.
When Rochelle proposed amending Rule 203(g)(l),
 adoption
of the same had been vacated along with Rule 204(c)(1) (Common-
wealth Edison v.
 Pollution Control Board,
 62 Ill.2d 494,
 343
N.E.2d 549 ai~Thsh1andChemical v.
 Pollution Control Board,
64 Ill.
 App.3d
 169,
 381 N,E,2d
 56)..
 Therefore, once docketed
this proposal was consolidated for hearing with R78—16,
 a Board
inquiry reviewing the rules on total suspended particulates
 (TSP).
On August 21,
 1980,
 R78—l6 was dismissed,
 Other than this pro-
posal by Rochelle, no steps were taken to adopt particulate
li~ciitationsfor fuel combustion sources until
 R82-1 was insti-
t~itedby the Board.
 Since further action
 in R82—l awaits receipt
of
 an economic impact study,
 Rochelle’s source
 is not currently
subject to a specific TSP emission limitation.
Consolidated with R77—15,
 R78—14, R78—l6 and R78—17, hear-
ings were held for R78—l5 on January 24,
 1979 in Springfield,
January
 30,
 1979
 in Chicago, February
 7,
 1979
 in Peoria and
April
 17,
 1979
 in Chicago.
 After receiving the economic impact
study from the Department of Energy and Natural Resources
 (then
the
Institute of Natural Resources) entitled “Economic Impact of
Sulfur Dioxide and Particulate Matter Regulations
 in Illinois,
R77—l5,” Doc. No.
 79—22, hearings were held on January
 29,
 1980
in Chicago, January
 30,
 1980 in Peoria and February
 13,
 1980 in
Chicago.
 The record closed on March
 17,
 1980.
Rochelle proposed this site—specific regulation primarily
due
 to
 the Illinois Environmental Protection Agency’s
 (Agency)
permitting policy in light of the Illinois Supreme Court decision
 vacating Rule 203(g)(1).
 This policy,
 as set out
 in “Guidelines
for the Performance of Air Quality Impact Analyses to he Used in
5 1-209
2
Support of Permit Applications,’ was to grant permits if sources
demonstrated either compliance with
 the
 terms
 of
 vacated
 Rule
203(g) (1) or compliance
 with
 ambient, air quality standards
(Petition, pg.
 2).
 This
 policy led
 Rochelle to conduct stack
tests to determine compliance with vacated Rule 203(g)(i)(B)
and modeling studies to determine its contribution to ambient
air concentration levels of particulate matter.
 The stack test
report, dated October, 1977, showed Rochelle’s contribution to
be an average emission rate of 0.418 lbs/mBtu or less.
 Since
the
 maximum
 rate allowable
 based
 on Rule 203(g)(i)(B) is 0.18
lbs/mBtu, Rochelle is petitioning for a site-specific rate of
0.60 lbs/mBtu.
The city’s plant produces electric
power
for its 12,000
consumers and produces
 process
 steam
 for
 a
 Swift
 and Company
facility.
 tts
 two steam
 boilers
 vent to a
 common
 stack
 and have
maximum rated capacities of 100,000 lbs/hour at 100 million Btu
per hour of heat input
 (R.
 376).
 Particulate matter emissions
are presently controlled through the use of mechanical collectors
(western precipitator multiclones) having 90
 efficiency, taken
together, when the boilers
 are
 operating at full loads
 (R. 377,
393, 398, 405).
Initially, Rochelle conducted six stack tests to determine
compliance with the 0.18 lbs/mBtu limitation.
 All resulted in
violations of that limit (Exhibit 5).
 The stack tests were then
averaged
 to
 provide
 a
 basis
 for
 modeling.
 Unfortunately,
 the
stack tests
 had
 not been conducted
 with
 the boilers operating
at
 full
 capacity,
 contrary
 to
 standard
 testing
 procedures.
Therefore
 the
 actual
 results
 were
 ratioed
 ‘up’
 in
 an
 effort
 to
characterize full
 load
 results.
 This was apparently done on the
 assumption
 that
 a given increase in heat input produces
 another
given increase in steam and a corresponding increase in emission
rates.
 The record reflects contrary opinions as to the success
of such extrapolation
 (R.
 400—405, 415—416).
Using
 the
 Posnt
 Source Diffusion Model (PSDM) Rochelle
further
 determined
 the
 maximum
 concentrations
 of
 TSP
 contributed
to
 the
 ambient
 air
 solely
 by
 its
 source.
 Worst
 case
 emission
rates were utilized
 to
 predict
 conservative
 ground
 level
 TSP
concentratations.
 Sequential
 calculations
 were
 made
 for 256
receptors located at various points ranging from 0.5 to 25.0
kilometers from the stack
 (R.
 387—388).
 This modeling indicated
that
 maximum
 TSP
 for
 the
 24_ho!r
 standard
 contributed
 by
 the
Rochelle
 facility
 is
 13.6
 ug/m
,
 less
 than
 11
 of the secondary
standard
 of
 150.0
 ug/m
 .
 This
 impact
 was
 predicted
 to
 occur
within
 1.5
 kilometers
 southwest
 of
 the
 plant.
 The
 maximum
 ca&—
culated annual contribution of the Rochelle plant is 2.3 ug/m1,
which is
 about
 4
 of the secondary annual standard of 60 ug/m’.
This
 impact
 was
 predicted
 to
 occur
 within
 1
•
5 kilometers north
of the plant
 (R. 388—389).
51-210
3
To further qualify the modeling results, Rochelle conducted
a
 monitoring
 program,
 intended
 primarily
 to
 determine
 background
values in the plant impact area.
 Monitoring at the modeled
northern
 impact
 point
 resulted
 in
 no
 violations
 of
 the
 annual
anbient air quality standards for TSP, and only one violation
 of the 24-hour standard.
 The latter was attributed to
nearby
road
 construction.
Rochelle conceded that control technology, either electro-
static precipitors (ESP) or baghouses, were available and
 that
installation would facilitate compliance with the 0.18 lbs/mBtu
limitation.
 Installation of baghouses was not considered by
Rochelle as a means to comply with the limit
 (R. 394—5); instal-
lation of ESP’s was considered, not as a substitute control mech-
anism,
 but
 instead as a means of further controlling Petitioner’s
existing cyclones
 (R.
 421).
 The capital cost to install ESP’s was
estimated at $1.4 million in 1977 dollars, or at a minimum average
cost of $100 per customer.
 These figures do not appear to be off—
set by monetary contribution by Swift and
Company as the primary
industrial user in the area.
The Rochelle facility is located in Ogle County
 which
 is
designated attainment for
 TSP
 at 40 CFR 81.314.
 The surrounding
counties,
 Lee
 and Boone, are likewise listed.
 However, the coun-
ties of DeXalb, Winnebago, specifically Rockford Township, are
listed as non—attainment for the secondary standard.
 In January,
1982
 the
 Agency
 proposed
 that Rockford Township
 and
 the Dexalb
County
 townships,
 except
 Dexalb
 and Mayfield
 townships,
 be
 redesig-
nated
 as
 attainment
 for
 the
 TSP
 secondary
 standard.
 Redesignation
of
 Rockford
 Township
 was
 based
 on monitoring done in that township,
whereas
 redesignation
 of
 the
 DeEalb
 County
 townships
 was
 based
 on
monitoring
 and
 modeling
 done
 in
 nearby
 townships.*
 During
 hearings,
DeTcaib Township, which did not then qualify for redesignation, was
of particular interest since it is twenty miles directly
east of
the Rochelle plant.
 Petitioner refuted any contribution by the
Rochelle facility to the non-attainment status stating that it
is
 ‘obvious
 that if no violations are predicted at 10 kilometers...
there would be no excursion for a receptor 20 kilometers away
(Exhibit 35, Part 1, pg.
 2).
 Additionally, the Illinois Environ-
mental Protection
 Agency
 (Agency)
 stated that
 it
 did
 not
 consider
Rochelle’s source to significantly contribute to ambient air
concentrations, and that the rural area of Ogle County is not
bothered by an air quality problem
 (R. 424).
 In post hearing
public
 comments
 the
 Agency
 stated that the relaxed limitation
‘would
 not cause the air quality problem.’
Over
the course of the years
 two
 monitoring
 stations
 have
been operated in DeRaIb Township.
 The monitoring results (Annual
Air Quality Reports 1977-1981) are set out in the chart below.*
51-211
4
Annual
 Geometric
 Annual
 Statistics
lea
 !~Sa!~es
 Mean
 Viol
 ations
~1503
 2603
 75
 60
ugim
 ugim
 ug/m
 ug/m
Total
 (Primary)
 (Secondary)
 1
 (Primary)
 (Secondary)
1977
 43
 1
 435
 103
 91
 56
 0
 0
1978
 34
 1
 0
 168
 111
 110
 +
1979
 26
 0
 0
 133
 96
 92
 +
 +
1979
 14
 0
 0
 95
 78
 66
 +
 +
1980
 29
 0
 0
 92
 84
 81
 +
 +
1981
 54
 0
 0
 129
 109
 98
 53
 0
 0
200
 S.
 4th
 St.
650
 N.
 1st St.
Insufficient
 data to determine annual geometric mean
Unfortunately, the statistical data for three
of
 the
 five
years
was insufficient to establish a geometric mean for eight
consecutive quarters, which is necessary for DeKaib
 Township,
and
nearby Mayfield Township to be proposed for redesignation.
Since this annual report,
 additional monitoring
data has
been
gathered which supports redesignation.
 In January of 1983 DeKalb
Township and Mayfield Townships were proposed for redesignation.*
Since
 the Rochelle facility has been operating at or near the
proposed emission limit and no violations of the standards have
been monitored,
 Petitioner’s statement that its source does not
impact DeKaIb appears valid.
The Rochelle stack
 is the only major fuel combustion emission
source in Ogle County emitting particulates
 (R,
 396),
 Keeping
 in
mind
that the modeling performed was conservative
and premised
on
a limit of 0,60 lbs/mBtu,
 the combined data from the
stack tests,
the PSDM and site~specificmonitoring indicates that
should the
liriitation requested be granted, violations of the
ambient air
quality
standard will not result.
However, in granting Rochelle emission limit more
relaxed
than
that presumably required by other such sources, the Peti-
tioner
will consume a portion of the Prevention
of Significant
Determinations
 (PSD) increments.
 Therefore,
 Rochelle
was
directed by the hearing officer to submit its estimation of the
amount of
 PSt) increments would be used up by this regulation
(R.
 411).
 The estimation was to be based upon the
emission rate
used
as input
 in the PSDM rather than the facility~sactual
emission rate.
 This information is contained in Exhibit 35.
Nevertheless, since no baseline has been established for
any
 areas affected by the Rochelle source,
 PSD increment
consumption
is
not sufficient reason to deny Rochelle a re~axed
site—specific
limitation~
*This information is taken from Agency publications
unavail-
able at hearings in this proceeding.
 The Board takes
official
notice of these publications
 in order to update air quality
information pertinent to this petition.
51-212
5
This rule was published for First Notice on November
19,
1982
 in
 6 Illinois ~~~ster
 14456
 —
 14458.
 On January
 6,
 1983
the Agency filed comments raising three
 issues, which Rochelle
responded
 to on January
 10,
 1983.
 No other public comments were
filed.
 i~t
the outset the Agency questions whether the record
which the Board based
 its decision on was sufficiently current.
Primarily the Agency is concerned that the supporting clocumenta—
tion offered by Rochelle at hearing may now be insufficient to
support a revision of the State Implementation Plan
 (SIP) by the
tinited States Environmental Protection Agency (USEPA).
 Acknowl-
edging that a SIP revision is necessary after a rule change,
this
 proceeding, however,
 need only justify a site—specific
rulemaking
by the Board.
 The analyses and documentation necessary for a
 SIP
revision,
 in this instance, can be provided to the Agency and the
USEPA during the SIP revision process.
 In
 its response, Rochelle
agreed that any additional
 information needed pertaining
 to the
SIP petition will he provided.
Lastly,
 the Agency retracts its support for the proposed
limitation of 0,60 lbs/mBtu because
 it is greater than the plant’s
actual emissions,
 and again because it is not sufficiently docu-
mented for the purpose of a SIP revision.
 As stated above,
 any
deficiencies
 in the SIP demonstration can be cured at that time.
In support of the more restrictive limit proposed
 in its comments,
the Agency relies on undocumented permit information and further
analysis of the stack test results.
 The Board’s decision to
grant
 0.60 lhs/mBtu was
 likewise premised on the stack tests,
 but
it was also premised on the modeling performed by Rochelle.
 The
modeling demonstrated that emissions up to 0.60 lbs/mBtu would
 not
jeopardize air quality.
The Board finds the evidence provided by Rochelle’s modeling
and monitoring sufficient,
 despite the questionable practice of
extrapolating the stack test results to full
 load capacity, to
demonstrate that this proposed regulation will not degrade the
attainment status of Ogle County or other nearby attainment areas,
The economic evidence indicates that although the technology
 is
available,
 it is costly.
 Swayed by evidence that the air quality~
and therefore the health or welfare of persons
 in the immediate
vicinity,
 is not jeopardized by the emission amount Rochelle
 seeks,
the limitation of 0,60 lbs/mBtu is granted.
ORDER
The following language
 is hereby proposed for adoption into
Chapter
 2:
 Air Pollution,
 Part
 II:
 Emission Standards and
Limitations for Stationary Sources:
RULE 203:
 Particulate Emission Standards and Limitations
(a)—(f)
 Unchanged.
51-213
6
(g)
 Fuel Combustion Emission Sources
(1)
 Using Solid Fuel Exclusively
(A)
 Existing Sources Located in the Chicago Major
Metropolitan Area——Reserved
(B)
 Existing Sources Located Outside the Chicago
Major Metropolitan Area——Reserved
(C)
 Exemptions for Existing Controlled Sources
Notwithstanding sub-paragraphs
 (A) and
 (B)
of this Rule 203(g)(l),
 any existing fuel
combustion emission source using solid
 fuel
exclusively, and meeting the following con-
ditions, may emit up to, hut not exceed,
 the
limits set out.
(i)
 As of ~p~il 14,
 1972 the emission source
has an emission rate based on original design
or equipment performance test conditions,
whichever is stricter, which is less than
0,2
 lbs/rnBtu of actual heat input,
 and the
emission control of such source
 is not
allowed to degrade more than 0.05 lbs/mBtu
from such original design or acceptance
performance test conditions, the rate of
emissions shall not exceed 0.2 lb~7ii~Eu
of actual heat input
 or
(ii)
 As of A~p~il
 14,
 1972 the source is
 in full
compliance with the terms and conditions of
a variance granted by the Board sufficient
to achieve an emission rate less than 0.2
lbs/mBtu, and construction has commenced on
equipment and modification prescribed under
that program;
 and emission control of such
sources
 is not allowed to degrade more than
0.05 lbs/mBtu from original design or equip-
ment performance test conditions whichever
is stricter,
 the rate of emission shall not
exceed
 0.2
 lbs/mBtu_2f
 actual
 heat
 input
 or
(iii)
 As of
 (the effective date of this Rule)
the rate of emissions_from Boilers
 #1 and #2
located at the Rochelle Municipal Steam Power
Plant,
 South Main Street, City of Rochelle
in Ogle County,
 Illinois shall not exceed
0,6
 lbs/mBtu of actual heat input.
51-214
7
IT
 IS SO ORDERED.
Chairman Dumelle and Board Member Werner concurred.
I,
 Christan
 L, Moffett, Clerk of the Illinois Pollution
Control Board, hereby certify tha~~he above Opinion and Order
was adopted on the
 ~fj~
day of
~7
t--&-~-’~-~-
 ,
 1983 by a
vote of
 ~
I:!
 /
~4p
 ~~___
Christan L. Moffett’,(~1erk
Illinois Pollution Control
 Board
51-215