1. 74-232
      2. 74-233

ILLINOIS POLLUTION CONTROL BOARD
December 5,
1986
IN THE MATTER OF:
)
GENERAL MOTORS
CORP.
)
PROPOSED AMENDMENTS
)
R83-7
TO 35
ILL.
ADM. CODE
)
900.103 AND 901.104
)
PROPOSED RULE.
SECOND NOTICE.
OPINION
AND
ORDER OF THE BOARD (by J. Anderson):
By action on November
7,
1985,
the Board proposed for first
notice certain
amendments to the Board’s rules and regulations
governing noise; publication
of the proposed amendments occurred
in the Illinois Register, Volume
10,
Issue
10, page
4175 et seq,
dated March 7,
1986.
The proposed amendments were occasioned by
a petition filed
by General Motors Corporation
(“GM”) on February
24,
1983,
and the record established by the Board through
hearings and submitted comments,
as specified
in the First Notice
Proposed Opinion, which is incorporated by reference herein.
Subsequent to publication of
the proposed amendments,
the
Board received three Public Comments
(“PC”): PC #3 filed May 7,
1986,
by the Midwest Environmental Assistance Center;
PC #4 filed
May 12,
1986, by Commonwealth Edison; and PC *5 filed June 30,
1986,
by GM.
Based on
a review of the record, as augmented by these
public comments,
the Board herein adopts for second notice
amendments only
to Sections 900.103(b)
and 901.104.
The proposed
First Notice amendments which would have established an
alternative measurement procedure are not being adopted for
second notices publication for
the reasons expressed in detail
below.
RATIONALE FOR THE PROPOSED AMENDMENTS
When the Board originally promulgated regulations
in 1973 to
control noise pollution
(In The Matter Of: Noise Pollution
Control Regulations, R72—2,
8 PCB 653 and
8 PCB 703),
it did
so
under
the premise that community response constituted the
principal test against which a noise was
to
be
judged as
polluting
or non—polluting.
The Board believes today,
as
it did
in 1973, that community response
is indeed
the appropriate test.
Several factors are involved
in the level
of community
response
to
a given noise.
An obvious factor
is the loudness
of
the noise.
The Board gave recognition to this factor when it
established
the current regulations by promulgating the maximum
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—2—
loudness
limits found at 35
ill.
Adm. Code 901.102 and 901.103;
these are unaltered under
the current proposed amendments.
A second factor
is the frequency of
sounds,
or pitch, with
certain frequencies having greater negative community response at
given loudness levels than others.
This factor
is also
recognized in
901.102 and 901.103 and remains unaltered under
the current proposed amendments.
It is also recognized in
restrictions on prominent discrete tones
(
901.106), which
likewise are not altered under the current proposal.
A third factor
is the duration
of the noise.
For example,
some noises have little negative community response even when the
noise
is moderately loud
if the noise occurs only rarely and for
short intervals.
Examples which have been cited are a dog bark,
a slammed car door,
and
a noon—hour factory whistle.
However,
the same noises may become highly objectionable
if repeated too
often.
Therefore, regulations based on community response should
correctly include provisions limiting the duration of noises.
Current Board noise regulations do recognize some aspects of
time—variation of
sounds.
These
include limitations on impulsive
sound
(
901.104),
including,
by separate amendments
in
1982 and
1983 respectively, special considerations for blasting noise
901.109);
and impact forging operations
(
901.105);
these
provisions remain unaltered under the current proposed
amendments.
However, current Board regulations fail
to give
consideration
to the general issue of fluctuating, time—variant
noises.
The reason is historical.
At the time of the 1973
rulemaking the state of acoustical
science and technology was
such that the ability to identify and quantify certain types of
noises
to accurately reflect community response, specifically
steady—state noises,
was generally agreed
upon.
This state of
conditions was reflected
in the standards as then recommended by
the American National Standards Institute,
Inc.
(“ANSI”)
for
noise control.
In promulgating its noise regulations,
the Board
relied upon ANSI and adopted
its then current recommendations,
and these remain the basis
of the Board’s current noise
regulations.
At that time the Board,
as did ANSI, also
recognized that the instrumentation had not yet been fully
developed and available
to properly reflect community response to
fluctuating noise.
However,
in ensuing years acoustical science and technology
has advanced
such that a new and more broadly encompassing method
of identifying and quantifying noise that better
reflects
community response has evolved.
Specifically, the ANSI
measurement procedure now reflects community response not only
for steady—state noise,
but also for fluctuating, time—variant
noise, after
correcting for ambient,
or background, noise.
It is
updating of the existing regulations to reflect this new
methodology which
is the principal
impetus for GM’s proposal and
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the Board’s proposed amendments.
In so doing, the Board believes
that compliance expectations and enforcement are enhanced by
utilizing current ANSI
based methodology and instrumentation for
fluctuating noise.
THE LEQ MEASUREMENT
The major proposed amendment to existing regulations
consists
of identification of the Leg (as defined at
35 Ill. Adm.
Code 900.101), with a one—hour reference time, as the measurement
which shall be utilized to determine compliance with the sound
emission standards of Part 901*.
The rationale for this
amendment is the determination that Leg is the most comprehensive
measurement of community response
to noise because
it best
combines consideration
of both steady—state and time—variant
noise.
This determination was detailed
in the the First Notice
Proposed Opinion and Order,
p. 9—12,
and therefore will not be
repeated here.
It
is significant to note that the loudness standards
of
Part 901, including both broad spectrum noises and noise
of
limited frequency range, are not altered by the proposed
amendments.
Moreover, for steady—state noises, measurement via
either present procedures or Leq will produce the same results.
It is only for fluctuating noises that the Leg measurement
provides
a deviation from the present rule.
This is done by
giving weight to both loudness and duration of the noise,
commensurate with considerations of community response.
CIRCUMSTANCES AT GM’S DANVILLE FACILITY
It
is not disputed that the impetus,
in part, for GM having
acted
to propose amendments
to the Board’s noise regulations
stems from difficulties it has experienced
in complying with the
existing
regulations at its Danville, Illinois, facility.
GM
contends that it wishes to respond to these difficulties.
However,
it also contends that,
given the fluctuating character
of its noise,
it does not know how to comply with regulations
where compliance is measured as
if the noise were steady—state.
GM further allows that promulgation of the proposed rule would
not necessarily bring facilities,
its own or others,
into
compliance.
Rather, GM believes that the proposed rule would
allow investment, where needed,
in control measures which would
assure compliance.
GM,
in essence, has asserted that its problem
is not due
to
its own special
site specific circumstances,
but,
rather,
is due
to a flow
in the regulation itself.
GM is asserting that all
emitters
of fluctuating noise are similarly situated,
in that the
*
An exception
is made for the sound emission standards of
901.109 due
to the special characteristics of noises considered
there.
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current Board regulations do not articulate the community
response related methodology for determining compliance.
CHANGES FROM THE FIRST NOTICE PROPOSAL
In its First Notice Opinion, the Board specifically
requested comments on the alternative justification procedure
embodied in proposed Sections 900.101, 900.l03(b)(2) and
901.130.
GM responded at length.
The Board
is persuaded, based
on GM’s response and its own further
reflection,
to remove the
alternative justification procedure from the proposed rule.
The proposed procedure reflected the Board’s concern as to
whether there might be value
in creating a separate procedural
mechanism,
utilizing the adjusted standard mechanism embodied
in
Section 28.1 of the Act.
The mechanism was potentially useful
for possible special noise situations,
where
a person might wish
to show that a different measurement procedure better correlates
to human response, notwithstanding the ANSI approach
of
correlating sound emission to community response.
GM asserted that the alternative measurement procedure may
have hidden pitfalls.
It pointed out that any procedure should
reflect community response;
to do otherwise is “likely to do what
the single—exceedence rule now does: measure emissions for
compliance with an arbitrary standard not based on community
response”.
(P.C.
#5,
p.
10)
GM pointed out that a correlation with human response will
always be inferior to the collective human testimony which forms
the basis
of community response, which in turn the Leg measures
numerically.
GM further asked the question: “in the presence of
a one—hour Leg, what will Rule 901.130
the
alternative
procedure
do for citizens that cannot be achieved in a nuisance
case under Rule 900.102?” (P.C.
#5,
p.
10)
The Board acknowledges that utilizing “human response” would
impart an inconsistent overlay on the Board’s regulations,
regulations which have always defined compliance
in terms of
community response.
And,
if the Board were to change
the
alternate demonstration so as to be based on community response,
rather than human response, there would be an even greater
question as to whether the procedure is a useful tool.
Leg is
the generally accepted best measurement of community response at
present.
If future developments and/or circumstances change this
situation, such a change would require
a full rulemaking
proceeding, since the change would be of general applicability.
On reflection,
the Board believes that the procedure would
not be a useful
tool, especially as measured against the Board’s
existing procedural mechanisms already available to any person
seeking a remedy,
e.g.
by way of an enforcement action
(based on
nuisance or otherwise),
a regulatory amendment, or a variance.
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—5—
Therefore,
the Board has deleted the proposed First Notice
language in Sections 900.101, 900.103(b)(2), and 901.130.
ECONOMIC CONSIDERATIONS
Two economically—based arguments
in opposition to the
proposed amendments have been reasserted
in the public
comments.
These relate
to the cost of replacing and/or adapting
existing noise meters such that these can measure Leg, and added
manpower needed to make noise measurements.
The noise meters presently owned by the Illinois
Environmental Protection Agency (“Agency”), and presumably at
least some of those owned by other entities who measure noise,
are not equipped to measure Leg.
Some confusion has existed
throughout the record in this matter as to the costs which would
be involved
in adapting these meters to Leg measurement.
The
latest estimate
is that the cost per meter would be approximately
$610
(PC 45, p.
14).
The Board does not believe that this cost
is prohibitive.
Moreover,
as existing meters require
replacement,
they would be expected
to be replaced by Leg—capable
meters anyway since these are the current standard of the
industry.
The Board also notes that the updated meters need be
used only for enforcement, not for routine assessment.
The gathering of one—hour Leq data suitable for enforcement
actions will,
under some circumstances, require longer
measurement times than required under
the present rule.
Thus,
manpower needs will be larger.
However, the Board believes that
this
is
a small price
to pay relative to the gains to be made
with respect to strengthening the noise regulations both as to
enforceability and compliance expectations.
ORDER
The Board directs that second notice of the following
proposed rule be submitted to the Joint Committee on
Administrative Rules:
Title
35:
Environmental Protection
Subtitle H:
Noise
Chapter
I:
Pollution Control Board
Section 900.103
Measurement Procedures
(a)
No change
(b)
Procedures Applicable Only to 35 Ill. Adm. Code 901
All measurements and all Urneasurement procedures to
determine whether emissions of sound comply with 35 Ill.
Adm. Code 901 shall be in substantial conformity with
ANSI S1.6—1967,
ANSI
Sl.4—l97l
——
Type
I Precision, ANSI
Sl.1l—1966 and ANSI Sl.13—197l
Field Method~,and shall,
74-233

—6—
with the exception of measurements to determine whether
emissions of sound comply with 35 Ill. Adm. Code
901.109,
be based on Leg averaging,
as defined
in
35
i~1l. Adm.
Code 900.101, using
a reference time of one
hour.
All such measurements and measurement procedures
shall correct or provide for the correction of such
emissions for the presence of ambient noise as defined
in ANSI Sl.13—l97l.
(c—e)
No change
Section 901.104
IMPULSIVE
SOUND
Except as elsewhere
in this Part provided, no person shall
cause or allow the emission of impulsive sound from any
property—line—noise—source located on any Class A,
B,
or C
land to any receiving Class A or B land which exceeds the
allowable A—weighted
sound levels7 ~
wt~i~
~
~m~e
e~ae~e~i~e7specified
in the following table when
measured at any point within such receiving Class A or
B
land, provided, however,
that no measurement of sound levels
shall
be made less than 25 feet such from property—line—
noise—source.
IT IS SO ORDERED.
3.
D. Dumelle and B.
Forcade dissented.
I, Dorothy M. Gunn, Clerk
of the Illinois Pollution Control
Board, hereby certify that the above Opinion and Order was
adopted on the
~T~-
day
of
/~c~4t-&,-’
,
1986 by
a vote
of
~
/~
Dorothy M. Gpnn,
Cler’k
Illinois Pollution Control Board
74.234

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