1. high barrier varies between $12 and $150 per linear foot (Ex. 6,
    2. Att. 4 and 5). For example, the U.S. Department of Transportation

ILLINOIS POLLUTION CONTROL
BOARD
August 28, 1975
In The Matte-c Of:
MOTOR RACING NOISE REGULATiONS
)
R74-14
OPINION AND ORDER OF THE BOARD
(by Dr. Odell)
BACKGROUND TO HEARINGS
On July
26,
1973, the Illinois Pollution Control Board
(Board)
adopted its Noise Regulations
(Chapter
8) which subject-
ed automobile and motorcycle racing
to the noise limitations set
out
in Rules 202
to 207 of that Regulation.
The compliance date,
pursuant to i~u1e209(j)
of Chapter
8, was set for August 10,
1975.
On September
25, 1974,
the Illinois Environmental Pro-
tection Agency
(Agency)
,
pursuant to Section
28
of the Illinois
Environmental Protection Act
(Act), proposed to amend Part II of
Chapter
8.
The Board designated the proposed amendment R74-14.
The proposal was intended to exempt motor racing from the specific
numerical limits contained in Part II of Chapter
8 between 7:00
a.m.
and 10:30 p.m.
Three hearings were held on the proposal:
May
7 and 14, and June
24,
1975.
The Board has authority to hold hearings and adopt
noise regulations based on language contained in Sections
25 and
27 of the Act.
The Agency proposed to exempt motorized racing from the
numerical limits because “the noise problems particular
to the
racing industry do not easily lend themselves
to the normal
solutions necessary for compliance with the property—line noise-
source limits established in Part II,~ of Chapt.er
8.
The Agency
believed that the primary methods of noise control,
i.e., en-
closures, barriers, treatment of the noise source itself, ac-
quisition of
!and buffer zones,
and ~pdrational
changes,would be
ineffective to bring about compliance with the regulations
in
Part
II of Chapter
8.
At the first hearing,
the Agency revised the language of
its proposed amendment to Chapter
8
(Ex.
1).
The revised
language,
contained in Exhibit 3,
stated:
18
415

—2—
“Rule 201:
CLASSIFICATION OF LAND ACCORDING TO USE
(a)
Class A Land
Class A land shall incluae ~ll land used as specified
by SLUCM Codes 110 through
190 inclusive,
651,
674,
681 bhrouqh
683 inclusive,
691,
711,
762,
7121,
7122,
7123
and 921.
(b)
Class
B Land
Class B land shall include all land used as specified
by
SLUCM Codes 397,
471 through 479 inclusive,
511
through
599
inclusive,
611 through
649 inclusive,
652 through
673 inclusive,
675,
692,
699,
7124,
7129,
719,
721,
722 except 7223,
723 through 761 inclusive
except 7311, 796 thro’~gh790 inclusive,
and 922.
(c)
Class C Land
Class C land shall include all land used as specified
by SLUCM Codes 211 through 299 inclusive,
311 through
396 inclus±ve, 399,
411
except 4111, 412 except 4121,
421,
422,
429,
441,
449,
460,
481 through
499 inclusive,
7123 and 7311 used for motorized racing,
and 811
through 890 inclusive.
(d)
A parcel or tract of land used as specified by SLUCM
Coda
81,
83,
91 or 922, when adjacent to Class
B or
C land may be classified similarly by action of a
municipal government having zoning jurisdiction over
such land.
Nothwithstanding any subsequent changes
in actual land use,
land so classified
shall retain
such B or
C classification until the municipal govern-
ment removes the classification adopted by it.”
“Rule
208:
LXCEPTIONS
(a)
Rules
202 through 207 inclusive shall not apply
to
sound emitted from land used as specified by SLUCM
Codes
110,
140,
190,
691,
and 742 except 7424 and
7425.
(b)
Rules
202
through 207 inclusive shall not apply
to
sound emitted from emergency warning devices and
unrequlated safety relief valves.
Cc)
Rules
202
through 207 inclusive shall not apply
to
sound emitted from lawn care maintenance equipment and
ac~ricultura1field machinery used during daytime
hours.
For the purposes of this sub—section, grain
dryers operated off the farm shall not be considered
agricultural field machinery.
(d)
Rules
202 through 207 inclusive shall not apply
to
sound emitted from equipment being used for con-
struc~ion.
18
416

—3—
Ce)
Rule 203 shall not apply to sound emitted from
existing property—line-noise-sources during night-
time hours,
provided, however, that sound emitted
from such existing property-line—noise-sources shall
be governed during nighttime hours
by the limits
specified
in Rule
202.
(f)
Rules
202 thi~ough207 inclusive shall not apply
to
sound emitted from land used as specified by SLUCM
Codes
7223 and 7ll1 when used for automobile and
motorcycle racing;
and, any land used for contests,
rallies,
time trials,
test runs or similar opera-
tions of any self-propelled device,
and, upon or by
which any person or property is or may be transported
or drawn, when ~:~chself-propelled device
is actually
being used for sport or recreation and
is actually
p~ticipating in an activity or event organized,
regulated,
and supervised under the sponsorship and
sanction of a club,
organization or corporation hav-
ing national or statewide recognition; PROVIDED,
however,
that the exceptions granted in this Rule
208(f)
shall not apply to automobile and motorcycle
racing, contests, rallies,
time trials,
test runs or
similar operations of any self—propelled device if
such activity is conducted between the hours
of
10:30
p.m.
to 7:00 a.m.,
local time.”
The Agency explained what the proposed amendments to Chapter
8 were intended to accomplish
(R.
15-20):
1.
Rule 201(b)
:
All motorized racing will become classi-
fied as
a Class C land-use so that all motorized racing activities
will be treated alike,
Tracks used for horse racing will be ex-
cluded from Rule 201(b)
and become unclassified
so that they will
be treated similarly to football and baseball events, which are
exempt under Rule 208(a),
SLUCM Code
742.
Fairgrounds will be
exempt from the numerical limits except when the land is used
for motorized racing.
2.
Rule 201(c)
:
Not only automobile and motorcycle racing
will be classified
as
a Class C land—use, but also other motorized
racing forms,
such as go-cart and snowmobile racing, will become
Class C land—use,
3.
208(a):
The exemption for fairgrounds
is deleted from
the numerical limits since the proposed amendment to Rule 201(b)
will achieve this result.
4.
Rule 20a(f):
Motorized racing
is exempted from the
numerical 1im~tsof Rules
202 through
207 between the hours of
7:00 a.m,
to 10:30 p.m.
The Rule provides “that the exemption
will only apply to vehicles being used for sport or recreation
and which are actually participating
in an activity or event
organized,
regulated,
and supervised under the sponsorship and
18
417

—4—
sanction of
a club,
orqanization or corporation having national
or statewide recoqnitionh
CR,
18).
The Agency noted that al-
though other industries are required to compJy by 10:00 p.m
under the night~imestandard, I0~30p.m.
is justified because
of the “particular uniqeeness of the racing industry.
Scheduled
racing events
for any particular evening are subject to un-
predictable delays because of both weather conditions and
accidents.
Furthermore.
~itis common practice for some race—
tracks to grade and c~e:i ~ieIi ta~cKsurface after the last
racing event.
The qra
~y
ar
caning process itself
is,
many times,
accomplisx1~asitu the use of motorized vehicles
which may not be caps
cci
r~ingwith the existing decibel
limits.
Therefore,
tie
~
nctustry is allowed an additional
30 minutes under
the
j~
~sal
~ account for unpredictable de-
lays inherent in the
a
L
self and for a cieanup process
which
in itself may
‘eta
CC)
SC
R,
19—20)
The Agency
stat
cast b
102 of Chapter
8, which
establishes a viola
easonable interference”
is
proven, would remain
till
ce and effect
arid would be
utilized by the Agen ~ ~.f~c~essary
(R,
20),
a
oNCh
Al
HEARINGS
Most of the tes~ •cry
ll
re hearings centered on the
issues
of feasibis
L,
fi~
~ to control noise emissions,
current levels of
~fj
a
race tracks,
and neighborhood
opposition to exentt
~
racing from the numerical
standards
in Chaprec
~
h~ t
~vidence will show, many questions
on the technical
pra’ ~
blli’y
ci~id economic reasonableness of re-
ducing emissions were
t ans rered.
Additional problems were en-
countered with noise
a~urem~nt~
because Chapter
8 standards
are expressed
in octa
e
and
so ~ä pressure levels
(dE)
while
most evidence submittect
‘ras ca~ essed
in A—weighted sound levels,
dB(A).
While such date
re vajuanle for comparison purposes,
the inability to convc
dB(A
the appropriate dB readings
limited the usefulness
sue
urca.
In addition,
the numerical
standards apply
to nolls
as
IIICSS
~ced on the receiving property
and do not include bar ~~ound
levels,
There are approx~L~ately125 to 150 motorized racing sites
in Illinois
(Ex.
12),
Given beaow are data for the major kinds
of motorized racing
act ivity in
tire state:
i~
Program
Track
Events involved
Kind of
tracic
Ii
time
surface ~er
session
Oval
30~-35 Eaenings
Asphalt/ 2-3 hours of
dirt
racing
Drag racing
10 12*
Day
Asphalt
3000 timed runs
Motorcycles
(scramble)
30
Day
Dirt
4 hour final
Motorcycles
(flat trac~-
Day
-
100 motorcycles
Tractor pulling
20~22 Lvenings
Dirt
2-6hr. elimina-
tion
*
There may be twice
~s nuricter of drag strips in Illinois
(R.
257)

—5—
The following table summarizes
the numerical regulations,
Rules
202 through 205,
in terms of dB(A)
equivalents
In
the
matter of Noise Pollution Control Regulations,
R72-9,
8 PCB 703,
29
(July 31,
1973)1:
dB(A)
for specified
emitting land uses
C
B
A
C
70
62
Receiving
B
66
62
55
land
use
A
(day)
61
55
55
A
(night)
51
45
45
Evidence
in Exhibit
6 stated that the primary noise sources
at racetracks arc the sounds emitted from the racing vehicles.
The typical racing vehicle, whether an automobile racing on an
oval track or a dragster,
is unmuffled and consequently produces
extremely loud A-weighted sound levels, dB(A),
in the near
vicinity of the track.
Secondary noise sources include both the
public address
3ystem and crowd cheering noises.
AnOther noise
source which
is present at some tracks
is the maintenance equip-
ment, which may include equipment for maintaining the track and
parking areas.
Oval racetrack data from Colorado recorded individual cars
with noise emissions of 95
to 110 dB(A)
at 100 feet
(Ex.
6, Att.
2)
Mufflers have effected al5
dB(A)
noise reduction.
Muffled
late
model cars emitted
82 dB(A)
600 feet from the racing path
(Ex.
6).
Data from Oregon indicate the unmuffled drag race cars emit
sound levels as high as 122 dB(A)
when measured
50 feet from the
vehicle path
(x.
6, Att.
1).
Tests of seven different mufflers
on individual late model stock cars showed emission levels be-
tween 84 to 103 dB(A)
at 100 feet, which prompted the Agency to
conclude that “you cannot generalize about cars and mufflers”
(R.
77)
The Agency stated that very little data were available on
performance standards
for mufflers and a specific automobile
(R.
92).
Wind speed and direction are also important factors
in
determining the effectiveness of mufflers
(Ex.
6, Racing Promotion
Monthly).
Some evidence
(Ex.
6, Att.
1)
indicated that mufflers
were feasible on drag racing cars.
Late model cars and dragsters,
both unmufflered, were recorded at 116 dB(A)
at 75 feet.
How-
ever with mufflers, drag race cars recorded “103 compared to
93
dB(A)
for stocks.”
The Agency introduced evidence on the feasibility of various
devices
to control noise emissions
(Ex.
6).
“Mufflers are available for racing motorcycles,
for racing
cars, drag race cars, and racing snowmobiles.
Application of the
mufflers
to racing cars will result in a significant noise re-
duction; however,
the results are not always the same.
Data
18— 419

—6—
measured from one vehicle, equipped with seven different
mufflers, during full throttle acceleration at a track indicate
that a noise reduction of from 4 to 20 dflA)
may
be achieved by
installing a muffler
CEx.
6, Att.
1).
The actual noise reductions
in dB(A)
at 50 feet obtained for the seven different mufflers
were:
4, 16 1/2,
18, 18 1/2, 19 and 20 dB(A).
The mean noise
reduction was 18 dB(A).
Some mufflers
are
more effective in re-
ducing noise emissions from racing vehicles
than
other mufflers.
The more effective racing mufflers will produce a noise re-
duction of approximately 15 dB(A) or more.
Mufflers installed on
drag race. cars are not as effective as mufflers.installed on cars
racing on oval tracks.
Data from eight drag cars reported in
Exhibit 6~Attachment 1 indicate that a noise reduction from 7 to
19 dB(A) was achieved with a mean value of 14 dB(A)
noise re-
duction.
The actual noise reduction for the eight drag cars
were 7, 12, 12, 13, 15, 16, 19 and 19 dB(A).
It is believed that
the mufflers on drag racing cars
are
not as effective since drag
racing cars operate at higher rpm’s
than
racing cars on oval
tracks and there is more mechanical noise on drag racing vehicles.”
As reported in Exhibit 6, Attachment 3, “mufflers which may
be used for racing vehicles cost between $10 to $40
per
car. The
actual costs~for three types of mufflers were $17.50 each, $40
per pair
and
$10 each.
These are 1974 prices and do not include
installation costs.”
One
expert
witness stated that certain classes of dragsters
were impossible to muffle
CR.
255).
Muffling restricts engine
exhaust and heat
flow
on engines aaready operatingEat
very-h4qh
temperatures.
The witness did not believe that the loss of
efficiency from muffling would
mean
significant engine heat re-
duction.
Rather, the use of mufflers would require heavy brác-
ing which would vitiate the effectiveness of the dragster
(R.
266,
7).
Few
scientific advances have been made in recent years on
metals to enable
them
to withstand higher temperatures
(R.
268).
At the present time tests are not being
conduc
ted to determine
possible methods to muffle dragsters
(R.
269).
Barriers have been applied at some racetracks; however,
the Agency believed that they are not an effective noise reducing
technique
(Ex.
6).
“To be effective, the barrier must be much
higher than the noise source and should be relatively close to
the noise source.
However, at raceLraèks the barrier can never
be very close to the racing vehicle, because for instance, at
times the vehicle will be on the opposite side of the track away
from the barrier.
Thus, because the barrier cannot be placed
near the racing vehicles,, they have in general proven to be an
ineffective noise reducing technique.
However, this is not to
preclude
the
possibility
that
a particular track and a particular
configuration may not benefit from
the
application of a barrier.
The cost of barriers depends upon
many
factors, including type
of barrier and height of barrier.
Data prepared for the con-
struction of highway barriers indicate that”the
-
cost for‘a 10~feet
high barrier varies between $12 and $150 per linear foot
(Ex.
6,
Att.
4 and 5).
For example, the U.S. Department of Transportation
estimates that a ten foot high barrier would cost $50
per
linear
15—420

foot for a 2:1 sodded earth berm;
$40 per linear foot for a
wood fence;
$38 per linear foot for
‘well liners;v and $100
per linear foot for a concrete wall.
A report published by
the Highway Research Board in 1973 lists the following approx-
imate costs per linear foot of
a 10
foot high barrier: $15 for
treated fir plywood panels;
$25 for an earth fill,
top soil and
sodded; and $30-55
for reinforced concrete.
The Illinois De-
partment of Transportation estimates that a sodded 2:1 earthen
berm, using
fill available
at the site, would cost $25 per foot
if the barrier were
10 feet high.
If the barrier were to be
20
feet high, the cost would become approximately $100 per linear
foot.
Using this latter information,
if
a track were to install
an earthen berm, using dirt available at its site, that were
500 feet long,
the installed cost would be $12,500 for a 10 feet
high berm an~$50,000 for a 20 feet high berm.
Depending upon
the configuration
of the particular track, a barrier
10
to
20
feet high could be expected to produce a noise reduction of 10
dB(A)
or less.”
“If the installation of mufflers and the erection of
barriers do not provide sufficient noise reduction to comply with
noise regulations,
the only other alternative is
to purchase
additional
land as a
‘buffer zone.’
Sound level data from Exhibit
6,
Attachments
1 and 2 indicate that racing cars equipped with
mufflers produce sound levels of 88-90 dB(A)
at 100 feet.
Using
acoustical propagation theory
(-6 dB(A)
per doubling of distance)
and assuming
a barrier were erected with a noise reduction of
10 dB(A),
there could be no residences for approximately one
quarter
of a mile from the racetrack for this single vehicle’s
noise emissions to comply with the Rule 202 sound pressure level
1 imits.
If the barrier were less effective and
if more vehicles
were operating,
a larger residence—free zone would be required
to achieve compliance.”
It would not be necessary to have
a
one—fourth mile “buffer
zone”
if the racetrack were
in
a rural
area or
if adjacent areas were zoned “Class C’~,pursuant to Rule
201 (d)
Testimony was offered on the economic impact of the re-
gulation.
Individuals involved with motorized racing generally
agreed that any substantial decrease
in noise would adversely
affect business.
The consensus of opinion was that spectators
not only come to the track to see competition but also were buy-
ing noise
(R.
130,
320).
However, other testimony indicated that
recent muffler iequirements
at some racetracks did not appear to
reduce participation.
Track operators felt that any limits be-
fore 10:30 p.m. would not permit them to complete a typical
nightly program.
While most operators strive to conclude racing
by 10:30 p.m.,
it
is very difficult to complete a racing program
by 10:00 p0m.
due to accidents, rain, delays,
and operational
difficulties
(R.
525).
A 10:00
p.m. closing would often mean
that the feature event could not be completed,
which creates
crowd hostility and, when rescheduled during the next session,
causes further difficulty in completing the subsequent racing
program on time.
The following economic data were supplied during the hear-
ings
(Ex.
19)
18
*
421

~Motor racing in Illinois contributes substantially
to the economy of the State:
1.
Over
5 million persons attended or participated in
some way.
2.
They spend or generate over $120 million per year
in
goods and services.
3.
They attend over
95 auto and 100 organized and regu-
lated
tracks,
4.
Twenty—five major county fairs sponsor motor races.
5.
Over 7,000 workers
in Illinois owe their livelihood
to the sport in which an additional 10,000 workers
are indirectly employed.
6.
Motor racing offers 10,000 drivers and 30,000 crew-
men a place to pursue their interests.
7.
There are 10,000 sports car enthusiasts who participate
in and through 325 clubs.
8.
There are 35,000 registered motorcycles in Illinois.
9.
The value of race tracks
is incalculable but probably
can be estimated as high as $50 million,
These tracks
pay millions in taxes
to local, county, state and
federal agencies as well as into general funds such as
Social Security and welfare programs.
10. There are 20,000 manufacturers,
distributors,
sales
groups,
retail stores,
speed shops,
and warehouses
involved in motor sports.
11.
To the best of my knowledge, only one track in Illinois
regularly holds events for SCCA sanctioned races
Blackhawk Farms, about
8 miles west of South Beloit,
Illinois,
This track has a full schedule of events on
virtually every weekend starting early in May and end-
ing
in October,
The number of participants probably
averages 150 per weekend with perhaps
4
to
5 times
this number
in crews,
families and workers.”
Testimony was offered that racetracks provide a proper outlet
for youthful energy through motorized racing
(R,
478).
Unless
such energies are exoended through the constructive activity of
track racing, such activities will occur on streets with more
serious social conse canoes,
The effects of motorized racing on
other industries was referred to.
Various protective features
associated with motorized racing have
benefited
society in various
ways
(P..
303).
It was also noted that neighboring states do not
have noise emissiu~nlimitations
so that drivers might be encouraged
to race elsewhere if numerical standards were enforced
(P..
530).
18— 422

—9—
Since August,
1970 the Agency has received a total of
26
individual unsolicited noise complaints involving motorized
racing activities at 14 racetracks
in Illinois.
The complaints
have been received from all parts of the state.
Noise readings
on homeowners’
property reveal the following levels of emissions
(Ex.
13)
Motorized
Ambient
Distance
Complaint No.
vehicles
dB(A)
reading
noise level
from track
72—22—1
Cars
75—84
53
73—6
Cars
78—80
1/4 mile
71—37
Cars
80—84
47—50
71—53
Motorcycle
84
72-24
Dragsters
78
54
72—15—1
Single cars
68—75
500 yards
The Agency stated that based on the information in Exhibit 13, none
of the tracks could comply with present standards.
Tests conduct-
ed by the Agency in May,
1975 at Rockford and Jacksonville speed-
ways were also found to be above compliance levels
(R.
507)
.
At
Jacksonville, late model cars
(20 vehicles)
required to have
mufflers were measured at
93
to 113 dB(A)
at
62 1/2 feet
(P..
504).
Not all cars were muffled,
and the Agency believed that total
muffling could reduce dB(A)’s by
5 to
8.
At 600 feet
(the nearest
residence)
noise levels exceeded
80 dB(A).
Similar but lower read-
ings were recorded at Rockford Speedway.
Most oval tracks
in Illinois have adopted some kind of
muffler requirement and many tracks have made adjustments
in their
public address systems
to limit noise emissions
(H.
567).
Such
changes may not bring tracks into compliance with the numerical
limits but may provide some relief to neighbors.
The muffler
requirements, however, do not set specific performance standards
but rather specify certain equipment as well as
satisfying the
requirements of a particular track operator.
For motorcycles,
the American Motorcycle Association has set a standard of
92 dB(A)
at
50 feet, which many tracks
in the state are voluntarily comply-
ing with
(P..
500,
501)
After the first hearing, the Board requested that the Agency
supply more detailed and complete information~onmotorized racing
in Illinois.
In the Board letter to the Agency on May 9,
1975
(Ex.
10), the Board stated that “Additional information is re-
quired on all the factors set out under Section
27 of the Act so
that the Board can carry out its statutory responsibilities
.
.
To develop a complete and accurate record the following inform-
ation must also be submitted.
For each track
in the state,
the
Board must know:
18
423

—10—
1.
Location of the track.
Is
it in
a residential or
rural area and what population centers are located
near it?
2.
The complaints
(by kind)
that have been received about
the noise at the track.
3.
The track surface.
4.
The primary and secondary uses made of the land
surrounding the racetrack,
5.
The approximate number of persons living within one
mile of the track.
6.
The approximate number of programs conducted at the
racetrack each year.”
During the June
24 hearing, the Agency answered the request
of the Board
(Comp.
Ex.
21)
“Russell
T.
Odell’s letter directed certain questions
to
the Agency.
Each question will be restated,
followed by the
Agency’ s response:
QUESTION
-
For each track in the state,
state the complaints
(by kind)
that have been received about the noise
at the track.
RESPONSE
-
Representative examples of the complaints the
Agency has received
is contained in this composite ex-
hibit as PART
1.
QUESTION
-
For each track in the state,
state the approximate
number of programs conducted each year.
RESPONSE
-
FCB Docket
No.
P.74-14, Exhibit No.
12 contains
information concerning the various categories of motoriz-
ed racing.
Exhibit No.
12 states both the approximate
hours of operation and days of the week during which events
are conducted.
Although Exhibit No.
12 does not give a
breakdown for each track,
it purports
to be representative
of racing activities
in general.
QUESTION
-
The Agency should present noise level data for several
representative
tracks
in the State of Illinois.
RESPONSE
-
This information has been supplied and is
a
part of
the record
of proceedings of PCB Docket No.
P.74—14 as
Exh~bit
No.
13.
QUESTION
-
If possible,
the Agency should supply noise level
data for Santa Fe Speedway.
RESPONSE
Nchse level data for Santa Fe Speedway is
included ner~H.nimmediately
following Russell T. Odell’s
letter of May 9, 1975.
The noise level data were taken
at a time when motorcycles were being
raced.
The Agency
424

—11—
does not currently have any sound level data for Santa
Fe Speedway at a time when cars were being raced.
“Russell
T. Odell~s letter of May
9, 1975 also included four other
questions which are specifically numbered in that letter as
questions numbered
1,
3,
4 and
5.
The Agency has not been able
to ascertain the information necessary to answer these four
questions.
The Agency does not know where every racetrack in
the state is located nor does the Agency know the names of the
various racetracks throughout the State of Illinois.
The re-
quested information could best be answered by the owners and
operators of racetracks throughout Illinois.
Since the racing
interests are represented through the Illinois Association of
Motor Sports
(AMS)
by legal counsel having an appearance on file
for PCB Docket No. R74-l4,
it is suggested that this information
could be obtained by the Board by way of either request or sub-
poena.”
Most citizens who testified at the hearings were opposed to
exempting motorized racing from the numerical limitations
in
Part II of Chapter
8
(H,
160—185; 335—350; 721—777;
and 810—835).
Most of these citizens lived within one mile of a racetrack and
expressed th’~following common complaints:
1.
Lawn, garden,
and patio activities after dinner are
disrupted by racing noise.
Indoor conversation, reading, and
relaxation are impaired by the noise.
2.
Citizens have had to buy air conditioning units because
evening indoor activities on racing nights require that the
house be closed-up.
3.
Noise from racetrack disrupts sleep and quiet con-
versation.
4.
Neighbors are reluctant to have evening parties on
racing nights because racing noise embarrasses them in front of
their guests.
5.
Traffic congestion,
air pollution, and litter problems
result from the motor racing activities.
Most witnesses in opposition to motor racing noise were not
opposed
to motor racing,
but as a “captive audience” felt that
they were entitled to relief from the excessive noise.
While
witnesses were not opposed to the noise generated by an occasional
passing train or airplane,
the incessant and continual sound from
the racing cars and public address system was considered ob-
jectionable.
For the most part,
track neighbors were not aware
of the serious nature of the noise emissions before they purchas-
ed their homes.
Citizens have not always been able to achieve adequate
relief on the local
level.
One witness testified on the success-
ful efforts
in her community to control motorcycle races at a
nearby track
(Ex.
7).
Another witness discussed the problem,
still unresolved,
of getting local agencies to act when the
agencies were unsure of who had jurisdiction over the facility
(P..
396)
18
425

—12—
FINDINGS OF THE BOARD
The record does not support a change in the regulation
because:
1.
The
technical data on noise abatement techniques
-
especially
in the important area of mufflers
-~
does not support
a regulatory change.
The Agency admitted that the information
was fragmented and incomplete.
While most manufacturers
presently have tests underway,
evidence on performance standards
was not made part of the record.
Some evidence suggested that
even dragsters could be muffled, but information to substantiate
or refute such generalities was not provided.
The problem of
analyzing
the data was compounded by the problem of converting
dBA’s into dE readings.
Had the rerord supported the conclusion
that noise abatement techniques were not available,
the frag-
mentary data would not havebeen adequate to establish a
different
numerical standard,
2.
Little economic data were presented into the
record.
Much of the data consisted of generaLstatements
on the numbers
of people directly or indirectly involved with motorized racing
in Illinois.
The evidence did not indicate how operators would
be affected by the regulation except
to say that they could not
comply
at all and therefore would all
presumably be out of
business.
However,
the record did
not support the statement that
compliance
was not feasible.
Many tracks, due to location, con-
trols, and racing limitations, may already
be in compliance.
In
future hearings
it would be helpful to point out how the present
standard
might affect operators who typify the kinds and conditions
of motor racing found statewide.
3.
The evidence is insufficient to enable the
Board
to
change
the present regulation in light of Section 27 of the Act.
Information required to be considered by the Board in adopting
a
regulation was not supplied although
requested on several
occasions, and much of the data submitted
was incomplete.
We
are
required to follow the legislative mandate in adopting
regulations.
Since conditions, tracks, cars, equipment,
etc.
are
widely
varied
in mototizedrac±ng, sufficient information must
be
supplied to give the Board
a
representative
picture of the
industry.
4.
Many citizens,
both in hearings
and during the public
comment period, strongly objected to the
Agency amendment,
It
is clear
that motorized racing seriously
interferes with and dis-
rupts
the homelife of many people.
While
the serious concerns
of suôh
citizens can beoutweiqhéd~by other more
serio~s-1nterésts,
the
record on this case does not convince
us that racetracks are
entitled to
greater righos
in the light of
the citizen objections.
The
homelife of an individual
is
one of his most important
interests;
the record does
not support a change to undermine or
limit this
substantial social interest,
426

—13—
5.
Some evidence was submitted which suggests that tho
present standard and methods of noise measurement may need to
be reviewed,
but not enough facLual data were provided
to
establish different standards.
On August 11, 1975,
the Agency
filed another proposed amendment to Chapter
8.
The proposed
amendment, docketed P.75—11 by the Board, deals with the same
subject matter of R74-14.
This proposed amendment will be
consolidated with R74—l4 and further hearings shall be held
as
soon
as possible.
In view of the questions raised concerning
current numerical limits, methods of measuring noise, and the
proposed amendment to Chapter
8 that was filed by the Agency on
August
11,
1975,
the Board will extend the compliance date
in
Rule 209(j) of Chapter
8 to February 10,
1976,
in order
to con-
sider these issues further.
Individual racetracks are not foreclosed from seeking
other relief.
First, under Section 37 of the Act,
the variance
procedure exists for any person.
While no racing facility has
ever sought a variance from the numerical limits,
relief
is
available
if sufficient proof can be shown.
Second,
under Rule
201(d)
of Chapter
8,
racetracks can implement zoning changes on
the local level and thereby protect themselves from residents
who move in after the racetrack is already situated
in the area.
Furthermore, pursuant to Rule 201(d)
racetracks can have adjacent
areas zoned “Class C”, thereby achieving exemption from the
limits set cut for Class A and B receiving land.
ORDER
IT
IS THE ORDER of the Illinois Pollution Control Board
that:
1.
The proposed amendment to Part
II of Chapter
8, con-
tained
in Exhibit
3 of R74—14
is hereby rejected.
2.
R74~l4 and P.75-11 are consolidated
and set for hear-
ing with the record in P.74—14 to be incorporated
in this new
proceeding.
3.
The compliance date in Rule 209(j)
of Chapter
8
is
hereby amended and extended to February 10,
1976.
I, Christan L. Moffett, Clerk of the Illinois Pollution Control
Board, hereby cert~4iythat the above Opinion and Order was
adopted on the
~t’1~
day of August,
1975,
by a vote of
3
p
.
Christan
L. Moffett, Cler
Illinois Pollution Control Board
18
427

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