1. 69.95
      2. 69-100
      3. 69-108

ILLINOIS POLLUTION CONTROL BOARD
April
10,
1986
IN THE MATTER OF:
R77—4
PUBLIC AIRPORT NOISE REGULATIONS
)
PART 904
PROPOSED RULE.
FIRST NOTICE.
PROPOSED OPINION AND ORDER OF THE BOARD
(by J.
Marlin):
This matter
comes before
the Illinois Pollution Control
Board upon
the filing by the
Illinois Attorney
General
on
February
16,
1977 of
a petition for adoption of airport noise
regulations at
35
Ill. Adm. Code Part 904.
Each of three
successive Illinois Attorney Generals
(William Scott,
Tyrone
Fahner
and Neil Hartigan) have sponsored
this proposal.
Specifically,
it
is
a proposal
to regulate noise emissions from
public airports that are owned
or operated by the State or
its
political subdivisions.
The proposal was published in the
Pollution Control Boardts Environmental Register
(No.
144, pp 5—
17, March 21,
1977).
Amendments
to the proposal were filed on
September 19,
1977
(Exhibit 23), June 12,
1978
(Exh.
127)
and on
November
14,
1979
(Exh.
156).
The Illinois Department of Energy
and Natural Resources
(DENR)
(formerly the Illinois Institute of
Natural Resources
IINR
and
th’e Illinois Institute for
Environmental Quality)
IIEQ
performed an economic impact
analysis on the proposal
and submitted four volumes of an
economic impact study
(EcIS)
to the Board.
Volumes
I and II
(public airports outside of Chicago) were filed on July
1,
1981
while volumes III and IV (public airports
in Chicago) were
filed
on November
16, 1981.
A total
of forty—five hearings were held
on the proposal:
thirty—nine merit hearings,
four economic impact hearings, and
two update merit hearings.
The last merit hearing
was
held
on
September
9, 1980,
the last economic impact hearing on March 15,
1983,
and the two update merit hearings were held on September 10
This Opinion and
the accompanying Order have benefited
from
considerable
input
from current Board Members.
The Board wishes
to acknowledge
the efforts
of the late Irvin G. Goodman, Vice
Chairman of the Board, who attended most of the hearings as
the
coordinating Board Member.
Current Board
staff who provided
invaluable assistance
in drafting the Opinion and Order
include
Kevin
F. Duerinck, who researched
the record and proposed initial
drafts;
Lee Cunningham, who prepared the first legal analysis;
Kathleen
M.
Crowley, who prepared the final
legal section; Morton
F.
Dorothy, who provided scientific and technical input;
Lorilyn
Chamberlin,
who provided editorial assistance,
and Beth Guido,
who typed
the several drafts.
69-65

—2—
and
18,
1985.
Prior
to these two update hearings, comments and
reply comments were filed by the participants,
the last being
filed on November
28, 1983.
After
the two update hearings, the
participants again submitted comments,
the last being
filed on
November
12, 1985.
The
record
in this proceeding consists of 46 transcripts
(approximately 7,500 pages),
253 numbered exhibits and
approximately 12
lettered exhibits,
4 EcIS volumes, written
public comments,
and additional filings.
Aside
from the two update merit
hearings,
the Board
is aware
that over
five years have passed
since the last merit hearing and
three since
the last economic
impact hearing.
This fact does not
seriously affect
the usefulness of the
record before
the Board.
Although some changes have occurred
in the number
of flights,
fleet mix, and individual companies and witnesses,
the basic
situation has not changed.
The two supplemental hearings held
in
September 1985 established that people living near airports
continue
to find the noise objectionable and that airports and
airlines maintain their objections
to the proposal.
Developing
an entirely new record would not serve a useful purpose.
The
Board
notes that references
to dollar amounts
in the record have
not been adjusted for any inflation that occurred since
the
testimony was given.
The two supplemental hearings held
in 1985 provided
participants the opportunity to raise any significant new
issues.
Further opportunity to comment will
be provided during
the
45 day first notice comment period.
Participants as well
as
the public will
be able
to comment
in writing on the Board’s
First Notice Opinion and Order
and may request a hearing.
To avoid
any confusion, citations to the hearing transcripts
will
be as follows:
~~RHfor merit hearing,
“E” for economic
impact hearing,
and
“5”
for
the two supplemental hearing
transcripts of September 1985.
Where
a hearing transcript was
not consecutively paginated,
any reference to
that transcript
is
by hearing date and page.
The Attorney General’s Office
(AGO) has proposed
to regulate
the amount of airport noise emanating from airports owned or
operated by the State
or
its political subdivisions.
The AGO’s
proposed noise standard
for receiving Class A Land
is
65 Ldn
(Ldn
is sometimes referred
to as DNL).
According
to the AGO, noise
in
excess
of this level
is unacceptable for land devoted
to Class A
uses.
Pursuant
to
35
Ill. Adm. Code 901.101(a),
Class A Land uses
include among others residential quarters, hotels and motels,
medical and other health services, correctional institutions,
schools,
religious activities,
certain cultural activities such
as
libraries and museums, nature exhibitions such as planetaria
69-66

—3—
and botanical gardens but not zoos,
leisure and ornamental parks,
and forest reserves.
The proposal phases
the
65 Ldn standard
in gradually over
seven years.
A variance procedure
is provided for airports which
cannot meet
the standard.
The variance procedure includes
developing
a plan for reducing noise at the airports.
In
addition,
the proposal requires airport proprietors
to gather
information on aircraft operations
to be used
in noise models
to
map the
area affected
by an airport’s noise.
The AGO’s proposal has been amended several times both
formally and
in the hearings and comments.
There
is no single
document
in
the record which contains the text of the rule as
proposed
by
the AGO at
the close of the hearings
in 1985.
The
Board
has used its discretion
to formulate the final wording.
At
the first hearing,
the AGO moved to incorporate
the
regulatory record
in R72—2,
In the Matter
of Noise Regulations
(R.
7—8) and R74—lO;
Motor Vehicle Noise,
(R.
132).
Over
objections
the motion was granted and the
records of both
proceedings were entered as Exhibits
2
and
3 respectively
(R.
7—
8,
R.
141).
The record
in R70—13,
the old Airport Noise
proceeding,
on motion
of the City of Chicago was entered
as
Exhibit
4
(R.
141).
The Board on its own motion hereby overrules
the hearing officer and strikes Exhibits
2,
3, and
4 from the
record.
These
three voluminous regulatory records have not been
considered
or cited by any participant.
Under
the circumstances,
the Board
sees no merit
in keeping
this bulk
in the record of
this proceeding.
Regarding jurisdiction, on May 12,
1977 the Board denied
the
Air Transport Association’s
(ATA)
and Chicago Association of
Commerce and Industry’s motions
for postponement
of the hearings
for deferral of briefing and consideration of constitutional and
statutory questions
(25 PCB 543, May 12,
1977).
At the time,
hearings were being held by the Federal Aviation Administration
(FAA)
based
on
a proposal filed
by the United States
Environmental Protection Agency (USEPA)
(25 PCB 541, May 12,
1977)
(25 PCB 545,
546,
May 12,
1977).
The Board will address
the jurisdictional as well
as other
legal
issues in the legal
section below.
Airport Noise Index
The Problem
5
The Legal Complexities of Airport Noise Regulation
7
Preemption Overview
8
Federal Statutes and FAA Regulations
9
Local Governments’ Attempts at Controls:
Ordinances and Litigation
14
69-67

—4—
Airport Proprietor’s Controls
18
Preemption As Affecting Board Regulatory
Authority
20
State Statutes As Affecting Board Regulatory
Authority
25
Citizen Concerns
31
Frequency of Flights
31
Impact of Noise on People’s Lives
31
Ground Noise
37
Noise Impact on Property Values
39
Industry Concerns
43
Development Patterns
53
People Move
to Airports
54
Airport Changes Impact Residents
56
Schools and Hospitals
60
Land Use and Zoning Concerns
61
65 Ldn Standard
66
Sound Measurement and Prediction
66
Acceptability of 65 Ldn as
a Standard
68
Noise Modelling and Monitoring
76
Effectiveness and Practicality of Noise
Reduction Methods
82
Retrofit, Replace and Reengirte
83
Takeoff and Landing Procedures
86
Preferential Runways
88
Taxiing
89
Engine Runups
89
Berms
90
Soundproofing
91
Easements
92
Purchase
92
Nighttime Curfew
& Reduced Operations
94
Land Use and Zoning
100
Alternate Airports
102
Economic Impact Study
103
Downstate Airports
104
O’Hare International
110
Midway
113
Discussion of Proposed Rule
115
Subpart A General Provisions
116
Subpart B Prohibitions
119
Subpart C Data Collection
121
Subpart D Exceptions
122
Subpart E Adjusted Standards and Procedures
123
69-68

—5--
THE PROBLEM
The
airport noise regulation
is one
of the most complex
issues ever
to come before
the Board.
The implications of any
decision will affect
a large number of competing interests and
government agencies at all levels.
The voluminous record and the
length of this Opinion are
a reflection of these realities.
Illinois
is home to
a number
of airports, including O’Hare
International which
is the busiest
in
the world.
The economic
impact of these facilities and related aviation activity
in
Illinois
in 1982 was over 9.1 billion dollars according
to the
Illinois Department of Transportation (Exh.
252,
b).
In 1984
O’Hare served 45.7 million passengers and processed over 882,000
tons of cargo with
a total
of 732,000 aircraft operations.
Its
closest rival,
Atlanta, handled 39 million passengers and 547,000
operations
(Exh.
240).
Because
of its location and many
connecting flights, O’Hare
has become
a pivotal point
for
the
world’s passenger and airfreight movements.
This facility plays
a key role in the economy of Illinois and
is essential to the
efficient operation of thousands of businesses.
Other publicly—owned airports
in the state may lack O’Hare’s
size, but make
a vital contribution
to the state’s economy.
They
provide
feeder service from cities which would otherwise
be
without air service and attract industries which depend on their
services.
The State’s airportsare expected
to increase their
operations over the coming decades.
Unfortunately, past airport
development has caused considerable conflict with local
residents
and in all probability future developments will have similar
problems.
With
the advent of commercial
jet aircraft
it became
apparent that much land surrounding airports would be subjected
to noise levels which would be unacceptable
for
a number
of uses,
including residential development, hospitals and schools.
The
noise
is generated by planes as they land and take off
as well
as
by engine testing and taxiing on the ground.
The noise pattern
about an airport
is irregular
in shape,
but generally follows
the
flight paths of the planes.
At a major airport such as O’Hare,
persons more than 20 miles from the runways may complain about
the noise
(R.
1009).
The testimony demonstrates that large numbers of people are
affected by the airport noise problem.
The two Chicago airports,
Midway and O’Hare, greatly impact
the surrounding areas.
Around
O’Hare, approximately 45,000 acres of land (exclusive of the
airport) were subjected to noise levels
in excess
of
65
Ldn.
At
Midway between 1,920 and 20,480 acres are impacted depending upon
the level of flight activity.
According to the EelS,
about
101,500 dwelling units are impacted by noise
at O’Hare and up
to
76,000
at Midway.
Over 500,000 people are subject
to noise
levels
in excess
of 65 Ldn from the two airports.
This number
69-69

—6—
varies
as
flight operations change
(Exh.
D).
Information
supplied by the City of Chicago’s Department of Aviation (CCDA)
illustrates how the amount
of land impacted by noise can change
over short time frames.
The data show that 1984 aircraft
operations exceeded 1982 operations
by over 100,000 yet impacted
ten fewer square miles.
According
to the CCDA,
about 50,000
fewer people were subjected to 65 Ldn in 1984 then
in
1979.
These estimates are based on population
and housing
unit counts
“based on residential units constructed
before or
in 1979.”
Table
1 summarizes the noise impact data provided by the CCDA
(Exh.
240).
As
of 1981,
downstate Illinois public airports created noise
levels
in excess of 65 Ldn on 8,614 acres, 962 acres of which
have noise sensitive land uses.
The 962 acre figure does not
include
industrial
lands, parks,
commercial
or airport properties
(Exh.
A,
EelS Vol.
I at 6).
Dwelling units
impacted totalled
2,575.
Id.
TABLE
1.
Population,
Community Facilities
& Square Miles
Within the
65 Ldn and Greater Sound Level*
1979
1982
1983
1984
Population
312,920
286,320
285,430
259,620
Housing Units
103,740
94,720
94,730
86,400
Schools
102
95
96
93
Hospital/Nursing Homes
15
16
20
14
Parks/Forest Preserves
115
105
102
103
Libraries
10
7
12
9
Square Miles
89
88
80
78
*
Population and housing
unit counts are based
on residential
units constructed before
or
in 1979.
O’Hare Total
Aircraft Operations
735,245
604,383
667,963
731,742
Source:
Exh.
240,
Map.
69.70

—7—
THE LEGAL COMPLEXITIES OF AIRPORT NOISE REGULATION
In brief summary,
the Attorney General has proposed that the
Board adopt regulations providing
for
a “continuum of actions”,
which he has characterized as
a three—tier system:
At
the
lowest
level
of
the
continuum,
State
action
simply
requires
the
disclosure
of
noise
impact
information.
At an intermediate level,
it requires the
use
of
such
information
and
forecasts
to
formulate
specific noise abatement policies and programs
as part
of
a
planning
process.
At
the
highest
level,
it
directs
state
intervention
and
the
use
of
state
authority
to
require
compliance
with
state
prescribed
standards,
whether
through
implementation
of
the
policies and programs formulated
at
the planning
level
or otherwise.
(A.G.
Brief,
p.
17—18).
The legal questions facing
the Board were well and simply
framed by Law Professor Sheldon Plager,
first witness
at the
first day
of hearing
in 1977:
First of
all,
is there
a role
for
the State of
Illinois
acting
through
its Pollution
Control
Board
and
its
Environmental
Protection
Agency,
in
the
abatement
of
this
airport
noise problem?
And
secondly,
if
there
is such
a
role,
is the proposal by the Attorney General
within the scope of that role?
(R.
12).
In summary,
the Board’s conclusions on each
of these
questions are
——
as were those of the witness
——
“yes, with
qualifications.”
In reaching these conclusions,
the Board has
considered the remarks of all hearing participants,
but has
placed particular reliance
on
the extensive and thoughtful
legal
analyses presented by the Attorney General
in support of the
regulation,
and
of the Air Transport Association of America
(ATA)
in opposition thereto.
The ATA argues that any regulation
by the Board
of airport
noise
is contrary
to both federal and state
law.
In brief,
the
ATA first contends that any regulatory action by Illinois
is
“preempted” by the United States Constitution, federal
legislation
and regulations
implementing that legislation.
The
ATA then asserts that,
even
if state
regulation of airport noise
is not preempted by federal law,
that the Board cannot adopt
rules without violating the laws and constitution of the State of
Illinois.
To place
these legal arguments
in perspective,
the Board
will
first outline the current state of controls of airport
noise, discussing case law as necessary to “tell
the story”.
The
Board will then address first the federal
law and then the state
law issues.
69-71

—8—
Preemption Overview
A preliminary overview of the general principles of
preemption analysis will serve
to enhance the discussion of
federal legislation and the regulatory reaction of the Federal
Aviation Administration (hereinafter
“FAA”)
to this legislation.
Simply stated,
the so—called “preemption doctrine”
is that
the federal government may take legislative
or regulatory action
which totally or partially precludes the states from legislating
or
regulating the same subject matter.
This doctrine flows from
the supremacy and interstate commerce clauses of the federal
constitution.
U.S. Const.
art.l
8, Cl.
3;
art 6,
cl.
2.
Due
to
the nature
and effects
of aircraft noise,
the principal cases
in
this area rely upon one,
the other,
or both of these
constitutional provisions.
In dealing with supremacy clause
issues,
the Supreme Court:
starts)
with
the
assumption
that
the historic police
powers
of
the
States
were not
to
be
superseded
by
the
Federal
Act
unless
that
was
the
clear
and
manifest
purpose
of Congress....Such
a purpose
may
be evidenced
in several ways.
The
scheme
of federal
regulation may
be
so
pervasive
as
to
make
reasonable
the
inference
that Congress left no room for the States
to supplement
it....Or the Act of Congress may touch
a field in which
the
federal
interest
is
so
dominant
that
the
federal
system will be assumed
to preclude enforcement
of state
laws on
the same subject....Likewise,
the object sought
to
be
attained
by the
federal law and the character
of
obligations
imposed
by
it
may
reveal
the
same
purpose....Or
the
state
policy
may
produce
a
result
inconsistent
with
the
objective
of
the
federal
statute.
Rice
v.
Santa
Fe
Elevator
Corp.,
331
U.S.
218, 230
(1946).
If purported state
intent and action runs afoul
of Congressional
intent and action
in any of these particulars,
the state action
will
be invalidated.
As to the commerce clause,
the basic principles,
as restated
by the Supreme Court
in Southern Pacific Co.
v.
Arizona,
325 U.
S.
761,
767
(1945), are that:
EJver
since Gibbons v.
Ogden,
9 Wheat.
1,
18241
the
states
have
not
been
deemed
to
have
authority
to
impede
substantially
the
free flow
of
commerce
from
state
to
state
or
to
regulate
those
phases
of
the
national
commerce
which,
because
of
the
need
for
national uniformity,
demand that their regulation,
if
any,
be prescribed by a single authority.
69-72

—9—
Generally,
the local benefit of
a state’s exercise
of its
police power
to protect the public health, safety,
and welfare is
examined
in relation
to the direct and indirect economic and
other effects which it may have on the national commerce.
Where
the burden
on interstate commerce
is
judged to
be excessive
in
relation
to the local benefit
a state seeks
to achieve, the
local
action
is
invalidated.
For
instance,
in Southern Pacific,
Arizona’s attempt
to reduce accidents by requiring that long
trains
be broken up
into shorter ones
for
travel through the
state was held
to be impermissible.
The safety interest causing
interruption
in service
to dissassemble and reassemble
trains was
found
to be plainly outweighed “by the interest of the nation in
an adequate, economical and efficient railway transportation
service”.
325 U.S.
at 783—4
Federal Statutes and FAA Regulations
The primary federal agency having jurisdiction of aircraft
and their
noise
is
the Federal Aviation Administration
(FAA),
created by the Federal Aviation Act (FA Act)
of
1958,
49 U.S.C.
1301 et seq.
The FAA was created primarily to promote air
safety
and commerce, functions formerly,
since
1938, within the
province of the Civil Aeronautics Board
(see
R.
19—20).
Section
1508 of the FA Act provides
in part
that the
“United States of
America is declared
to possess and exercise exclusive national
sovereignty
in the airspace
of the United States”.
Sections
1348(a)
and
(c) give the Administrator of the FAA wide authority
to promulgate regulations.
Th& 1958 FA Act did not specifically
mention the regulation
of noise, but a 1968 amendment, Pub.
L.
90—411, added Section 611
(49 USC
1431) which provided that:
to afford present and future relief and protection
to
the public
from unnecessary
aircraft
noise and sonic
boom,
the
Administrator
shall
prescribe
and
amend
such rules...necessary to provide for
the control and
abatement
of aircraft noise and sonic
boom.
The FAA’s regulatory response
to Section 611 was the
promulgation
of Federal Aviation Regulations
(FAR)
14 C.F.R. Part
36
(hereinafter “FAR—36”).
In brief,
FAR—36
set
a limit
on noise
emissions
from domestically manufactured new aircraft for which
manufacturers were required
to have aircraft certificates.
FAR—
36 was not applicable
to aircraft types approved as of November
18,
1969, and was not applicable
to all
newly manufactured
aircraft until 1973.
In 1972,
Section
611
of the FA Act was amended by the Noise
Control Act of 1972 (hearinafter “Noise Control Act”).
Pub.
L.
92—574, codified
at 42 U.S.C.
4901—4918.
The
FAA
characterized
this action as one taken by a Congress “displaying some
dissatisfaction with
the FAA’s methodical regulatory practice
under Section 611”
(Exh.
13,
p.
30).
The amended Section 611
added USEPA to
the
FAA
rulemaking process, although
it did not
give the USEPA independent authority to promulgate
69.73

—10—
aircraft/airport noise regulations.
Instead,
and
in brief,
the
USEPA was authorized and directed
to present regulatory proposals
to the FAA.
The FAA was required only to publish
the proposals
in the Federal Register and,
after
considering public comments
thereon,
to advise
the public whether
it was adopting any
proposals.
Section 611 was also amended
to require the FAA to
consider noise abatement
in
its
issuance of aircraft
certificates.
As discussed
later
in more detail, consideration of
the
legislative history of the FA Act and the Noise Control Act led
the Supreme Court
to remark in City
of Burbank
v. Lockheed, 411
U.S. 624,
639
(1973)
that:
Control
of
noise
is
of
course
deepseated
in
the
police
powers
of
the
States.
Yet
the
pervasive
control
vested
in
EPA
and
in
FAA
under
the
1972
Noise
Pollution
Control
Act
seems
to
leave
us
no
room for
local curfews
or other
local controls.
What
the ultimate
remedy may
be
for
aircraft
noise
which
plagues
many
communities
and
tens
of
thousands
of
people is not known.
The Burbank case, which invalidated
a city’s attempt
to impose
a
curfew on night—time flights into a private airport,
is the
Supreme Court’s first
and
last word
on the subject.
However,
Burbank
is as significant for what
it did not address,
as what it
did address.
In footnote
14
to the opinion, the Court first
quoted a letter from the Secretary of Transportation concerning
his view of the effects
of Section 611 on the
rights of
governments as proprietors of
airports.
The Court itself then
stated
that:
We
are
concerned here
not with
an
ordinance
imposed
by
the
City
of
Burbank
as
“proprietor”
of
the
airport,
but
with
the
exercise
of
police
power.
While
the Hollywood—Burbank
Airport may
be
the
only
major airport which
is privately owned, many airports
are owned
by
one municipality yet physically located
in
another.
For
example,
the
principal
airport
serving
Cincinnati
is
located
in
Kentucky.
Thus,
authority that
a municipality may have
as
a
landlord
is
not necessarily
congruent with
its police
power.
We do not consider here what limits,
if
any, apply to
a municipality as
a proprietor.
(411 U.S.
at 635.)
Since
1973,
FAR—36 and the companion FAR—91
(which sets
complaince deadlines for FAR—36)
remain
the only regulatory
limits on noise emissions promulgated by the FAA.*
In 1976,
the
*As of July 1,
1985,
88
of
the United States certificated fleet
were
in compliance with the noise certification standards of FAR—
36;
100
compliance
is required by statute on January
1,
1988
(continued)
69.74

—11—
FAA developed
its Noise Abatement Policy
(hereinafter
“Noise
Policy”).
The Noise Policy encouraged
the airport proprietor
to
take various voluntary actions, on the basis of the
FAA’S
assessment that
it
is the proprietor who was
“primarily
responsible
for planning and implementing actions designed to
reduce the effect
of noise
on residents of the surrounding
area.”
(Noise Policy,
Exh.
13,
p.
5).
In support
of this
position,
the FAA cited three cases
(to be discussed in more
detail later) which
it characterized as setting forth
the
responsibilities
of airport proprietors.
It was noted that
Griggs
v. Allegheny,
369 U.S. 84
(1962) established
the
proposition that proprietors are liable for payment
of damages
for noise
resulting from aircraft operations.
The
FAA
then cited
Air Transport Assn.
v.
Crotti,
389 F.Supp.
58
(N.D.
Cal. 1975)
as
establishing that:
The
airport
proprietor
is
responsible
for
the
consequences which
attend
his operation
of
a
public
airport;
his
right
to control
the use of
the airport
is a necessary concomitant, whether
it
be directed by
state
police
power
or
by
his
own
initiative...A
correlating
right
of
proprietorship
control
is
recognized
and
exempted
from
judicially
declared
federal
preemption
by
footnote
14
of
the
Burbank
opinion
.
Manifestly,
such
proprietary
control
necessarily includes the basic
right
to determine the
type
of
air
service
a given airport proprietor wants
its
facilities
to
provide;
as
well
as
the
type
of
aircraft
to
utilize
those
facilities...(389
F.Supp.
at 63—64.)
Finally,
the FAA also noted that the “Crotti principle” had been
followed in the then recent decision
in National Aviation
v. Cit~
of Hayward, 418 F.Supp.
417
(N.D. Cal.
1976).
In that case,
the
City had by ordinance imposed
a curfew at the airport which it
operated.
The Hayward court examined the
legislative history of
the amendments
to the FA Act and concluded that these amendments
were not designed
to prevent airport proprietors from excluding
(Exh.
231,
at 1—2,
and app. 1).
Noise standards for foreign aircraft are set by the International
Civil Aviation Organization
(ICAO),
of which
the United States
is
a member.
The ICAO adopted noise
standards in April
1971,
known
as “Annex 16”
(R.
4392).
(The U.S. version of Annex
16
is Part
36).
Foreign air carriers must
at least meet the Annex 16
standards if they desire
to operate
in the U.S.
When the ICAO
did not enact
a compliance timetable for Annex
16 by January
1,
1980,
the FAA did pursuant
to the Aviation Safety and Noise
Abatement Act of 1979.
Foreign stage II aircraft must meet the
Annex
16 standards by January 1,
1985
(14 CFR 91.301,
14 CFR
91.303, November
28,
1980).
However,
exemptions
are available
from this deadline.
69-75

—12—
aircraft on the basis
of noise considerations.
The Hayward court
also found
that,
to the extent that the curfew ordinance could
cause
the plaintiff air freight company
to use another airport
between 11 p.m.
and
7 a.m.,
that the City action did have an
effect on interstate commerce.
However,
the court did not find
the curfew invalid for that reason,
as the effect was:
incidental
at
best
and
clearly
not
excessive
when
weighed
against
the
legitimate
and
concededly
laudable goal
of
controlling
the noise
levels
at the
Hayward Air Terminal
during
late evening and morning
hours.
(418 F.Supp.
at
427)
The FAA’S synthesis of these cases was that:
The
power
thus
left
to
the
proprietor
to
control
what
types
of
aircraft
use
its
airports,
to
impose
curfews
or
other
use
restrictions,
and,
subject
to
FAA
approval,
to
regulate
runway
use
and
flight
paths,
is
not
unlimited.
Though
not
preempted,
the
proprietor
is subject
to two important Constitutional
restrictions.
He
first may not take any action
that
imposes
an
undue
burden
on
interstate
or
foreign
commerce
and,
second
may
not
unjustly
discriminate
between different categories of airport users....
The
~j~yward court
indicated
that
the
FAA
had
the
authority
to preempt proprietor
regulation.
We have
been
urged
to
undertake
-
and
have
considered
carefully
and
rejected
full
and
complete
federal
preemption
of
the
field
of
aviation
noise
abatement.
In our judgment the control and reduction
of
airport
noise must
remain
a shared responsibility
among
airport
proprietors,
users,
and
governments.
(Noise Policy,
Exh.
13,
p.
33—34)
The FAA did note,
however,
its “substantial power
to
influence
airport development” through its grant—in—aid program pursuant
to
the Airport and Airway Development Act,
49 USC
1701 et seq.,
which provided
it with new authority to share
in the costs
of
certain noise abatement activities.
The Noise Policy went on
to
specify what an airport proprietor
might wish
to include
in a
noise abatement plan, suggesting actions that
a proprietor could
take directly, those
it could propose
to local governments,
those
it could propose
to FAA for
implementation, and those
it could
propose
to the airlines
it services.
(Exh.
13,
p.
55—57)
In
short,
the FAA encouraged,
but did not require, noise abatement
planning subject
to
its veto
as regards proposed adjustments
in
operational
controls.
This policy
of leaving affirmative noise control actions
to
proprietors has since been formalized in FAR rules codified at
14
CFR Part 150
(hereinafter “FAR—lSO”).
See “interim rule”,
46
Fed. Reg.
8316, January 26,
1981,
and final rule,
49 Fed. Reg.
49269,
December
18, 1984.
69-76

—13—
FAR—iSO was adopted
in part to implement mandates contained
in the Aviation Safety and Noise Abatement Act (ASNA Act)
of
1979, 42 U.S.C.
2101 et seq., as well
as Section 1431 of
the
FA
Act.
The ASNA Act provided that on or before February 28,
1981,
the Secretary of Transportation should by regulation
(1)
establish
a single system for determining the exposure of
individuals
to airport noise; and
(2)
identify land uses
compatible with various exposures of
individuals
to noise.
49
U.S.C.
2102.
Once these
regulations were established, any
airport operator could submit a “noise exposure map”
to the
Secretary,
setting forth existing and projected non—compatible
land uses
in the area surrounding the airport.
49 U.S.C.
2103.
Thereafter,
the airport operator could
then submit
a
“noise compatibility program” setting forth the measures the
operator has taken or proposes to reduce existing, and prevent
future, non—compatible uses within the area covered by the map.
49
U.S.C.
2104(a).
The Secretary was
required
to approve
or
disapprove any programs submitted
to him
in accordance with the
criteria set forth
in
the ASNA Act.
49 U.S.C.
2104(b).
In FAR—l50,
the FAA adopted the noise measurement system
known as
the Ldn metric.
FAR—l50 further establishes
the
procedures,
standards and methodology for the development and
submission
of noise exposure maps and airport noise compatibility
programs, and sets forth the criteria to be employed by the FAA
in determining whether
to approve or disapprove
the
maps/programs.
Approval by the
FAA
of
a noise compatibility
program “does
not direct any implementing action.”
14 CFR Part
150.5(c).
Moreover,
in some instances proprietors must request
“federal
actions”
to implement specific measures of
a program,
which, where appropriate will include an environmental assessment
of the proposed action.
In considering
the voluntary Part
150 program,
it
is
particularly important to note the limitations contained
in the
ASNA Act.
Section
2106 provides that any noise exposure map and
related data submitted
to the FAA may not be “admitted as
evidence, or used
for
any other purpose,
in any action seeking
damages
or other
relief for
the noise that results from the
operation of an airport.”
At the same time, Section 2107
provides that a person acquiring property
in an area surrounding
an airport with respect to which
a noise exposure plan has been
submitted may not recover damages for noise
“if such person had
actual
or constructive knowledge of the existence
of the noise
exposure map”,
absent “significant change”
in airport operations
or layout.
In conclusion,
the Board notes
that
the FAA has been
characterized by one witness
in this proceeding as the “reluctant
dragon” of airport
noise control
(R.21).
The FAA’s posture does
not appear likely to change, given that at
least one federal
circuit court of appeals has agreed with
the
FAA’s
interpretation
that Section 611 of the FA Act, imposes a discretionary, and not
69-77

—14—
a mandatory, duty on the FAA
to control airport noise.
The
comments made by the court
in Di Perri
v.
FAA,
671
F.
2d
54,
56
(1st Cir.
1982)
remain as true today
as
they were
in 1982:
...while
section
1431
may
empower
the
FAA
to
promulgate
airport
noise
regulations,
the agency has
not done
so.
There
are,
in
fact,
so far
as
we
can
determine,
no
airport
(as opposed
to aircraft) noise
abatement regulations presently in effect pursuant
to
this
authority.
The
FAA has so
far elected
to limit
its
regulation
of
aircraft
noise
primarily
to
noise
abatement
design
criteria
for
new
aircraft.
See,
e.g.,
14
CFR Sections
36
and
91.301—311.
In
these
regulations,
the
FAA
has
been
careful
to
avoid
exercising
authority
over airport
noise.
(original
emphasis, footnote omitted)
Local Governments’ Attempts At Controls: Ordinances and
Litigation
In adopting Illinois’
first noise regulations,
the Board
specifically excluded airport noise from their coverage, with the
intent
of initiating later regulatory proceedings.
See, In The
Matter
of Noise
Pollution
Control Regulations, R72—2, Opinion of
July 31,
1973
(8 PCB 703
at
704,
722),
(noting that the Board’s
focus on the area of noise
in general was initiated by
a proposal
to regulate airport noise).
In, the absence of state regulations
in this
arena, governmental attempts
to control
or abate airport
and aircraft noise have been the province of the municipal and
county governments.
Local
governments whose populations are impacted by airport
noise fall into two classes:
those which are themselves airport
proprietors, and those which are neighbors of airports operated
by other entities.
Under Burbank,
a proprietor—government may
exercise direct control of
its airport
to the extent
constitutionally permissible
(as described
in detail later).
However,
the Burbank decision has precluded use of the
traditional police powers over noise.
While
local governments
may still regulate land use,
the record
in this proceeding amply
indicates that land use controls have not been very effective.
As summarized by the Attorney General:
In
some
instances
pre—existing
incompatible
uses
limited
the effectiveness
of
land use controls.
(R.
18;
R.
45).
In other
instances affected communities
were
not
privy
to
the
airport’s
data
relative
to
current and/or
future operations
that were needed
to
enact
appropriate
controls
(R.
18;
R.
183;
R.
235—
236;
R.
1055—1056
and
1065;
R
4911;
R
5073).
Moreover,
where
this
data
was
available
its
utilization
by
local
zoning
authorities
was
not
assured.
(Cf.
R.
2062—2063 with
R.
1402—1409 and
R.
1848.)
A.G. Comments,
p.
9.
69-78

—15—
The
ineffectiveness
of attempts
by non—proprietors to exert
police powers
is exemplified
by some of Illinois’ airport noise
litigation.
In Village of Bensenville,
et
al.
v.
City of
Chicago,
16 Ill.App.3d 733,
306 N.E.2d 562
(1st Dist.
1973),
Bensenville and other
communities surrounding O’Hare Airport
alleged
that aircraft operations from the airport emitted noise
and air pollution over the communities so as
to constitute
a
public nuisance.
Bensenville therefore sought an injunction
prohibiting Chicago from
1) expanding the airport
in such a
manner
as
to expose
the communities
to higher noise levels,
2)
allowing
the airport’s facilities to
be utilized by any aircraft
which emit noise beyond
a certain level and
3) permitting any
aircraft which produce noise
in excess of a certain level to
utilize airport
facilities unless such aircraft was
in use prior
to the date
of the requested relief.
Remarking that
the
“real thrust”
of the complaint was
to
prohibit aircraft while
in flight over the communities from
producing noise
in excess of prescribed limits,
the court found
the matter before
it was controlled by the Burbank decision
(which was
then some six months
old).
After extensively quoting
that decision,
the court held that under the Federal Aviation
Act,
as amended
by the Noise Control Act of 1972,
the federal
government had, “so occupied the regulation of aircraft noise and
air pollution
as
to preempt any state or local action
in that
field.”
306 N.E.2d at 566.
In County of Cook
v. Priester,
22 Ill.App.3d
964,
318 N.E.2d
327
(1st Dist.
1974),
affirmed without
reaching the supremacI
clause
issue,
62
Ill.2d
357,
342 N.E.2d 41
(1976),
the issue was
whether
a county, pursuant
to conditions imposed
in
a special use
permit issued under
its
zoning ordinance,
could lawfully impose
a
weight limitation on aircraft using a private airport.
Specifically,
one such condition sought to
restrict usage of one
of the airport’s runways
to aircraft that did not exceed 60,000
pounds.
In attempting
to justify that condition,
the County argued
that the limitation was
a safety
factor for the surrounding
landowners,
users,
and passengers of users of the airport.
As
such,
the County maintained that
it had a legitimate interest and
duty
in protecting the citizens living
in the area surrounding
the airport,
and was free to regulate activities within its
boundaries
to that end.
The Appellate Court disagreed,
remarking first
that the
County had failed
to show how the safety of
the public was
impaired by aircraft over 60,000 pounds utilizing the airport.
After reviewing the federal aviation statutory scheme,
including
49 U.S.C.
Sections 1508 and 1348,
and relying on the Burbank
decision,
the court determined that the condition was
unenforceable.
Specifically,
the court viewed the condition as
an attempt
to manipulate the type and number
of aircraft
servicing the airport
by regulating air traffic beyond
the
69.79

—16—
boundaries
of the county under
the guise of land use controls.
Finding
that the effect of the condition on the use of navigable
airspace was comparable to that cited
in Burbank,
the court held:
“that the level of
federal regulation of air commerce
by
the
Federal Aviation Agency
sic
is
so pervasive
as
to deprive
other
governmental bodies of
the power
to
act,
and
that
the
weight
limitation
ordinance
violates
the
Supremacy
clause
of
Article
VI
of
the
Constitution
of
the
United
States.”
318
N.E.2d
at
332.
The Board notes
that these holdings are squarely
in line
with
those
in other jurisdictions invalidating attempts by non—
proprietors to mandate
or preclude some specified actions
by the
airport proprietor which would have
a direct effect upon airport
operations.
These are,
by way
of example, San Diego Unified
p~9~Authority v. Gianturco, 651 F.2d 1306
(9th Cir.
1981)
(curfew); Luedtke v
.
County
of Milwaukee,
521
F.2d 387
(7th Cir.
1975)
(number
of flights, hours of operation,
aircraft operating
procedures and flight paths);
U.S.A.
v. City
of Blue Ash, Ohio,
487 F.Supp.
135
(S.D. Ohio
1978), aff’d
621 F.2d 227
(6th Cir.
1980)
(mandating
turns after takeoff) Northeast Phoenix
Homeowners, Assn.
v.
Scottsdale Municipal Airport, 636; F.2d 1269
(Ariz. App.
1981)
(restraining runway extension,
curfew and
specific operating procedures),
Air Transport Assn.
v.
Crotti,
supra,
(SENEL noise limits directly applicable to aircraft in
flight
as discussed
in more detail below).
Not all local attempts to
regulate in areas which may impact
airports fail, however,
as evidenced by LaSalle National Bank
v.
County
of Cook,
34 Ill.App.3d
264, 340 N.E.2d
79
(1st Dist.
1975).
At issue
in that case was whether a Cook County zoning
ordinance which limited building heights for areas within two
miles
of designated airports had been preempted by FAA
regulations concerning airport approach zones.
The allowable
height of any building under both the ordinance and
the FAA
regulation was based on the distance of
the building from
a given
measuring point.
Under the County ordinance, however,
that
measuring point was
the airport boundary, while under
the
FAA
regulation
it was the end of
the runway.
From these measuring
points further but differing computations under both the
ordinance and regulation were required
to determine
the allowable
height.
In upholding the Cook County ordinance,
the court
first
discussed the Priester decision, which held that regulation of
the field of air commerce had been federally preempted.
The
Court determined, however,
that it was not air
commerce, but
instead the construction
of buildings,
that was the object of
control by the county ordinance.
Accordingly, preemption was not
at issue
as the goals of the federal and
local government were
different.
Specifically,
the court found that while the FAA was
concerned with air
traffic safety,
the County was concerned with
69.80

—17—
the health,
welfare and
safety of those near the air field.
34
Ill.App.3d,
at 274—5;
340 N.E.2d at 87—88;
accord, Praznik
v.
Sport Aero,
Inc.,
42 Ill.App.3d
330,
355 N.E.2d 694 (1st Dist.
1976)
(state aircraft guest statute was not preempted by FAA
safety regulations).
Finding
themselves powerless
to limit airport noise and
expansion,
governmental entities have banded together
to ask the
courts
to do so,
using various
legal
theories.
In Illinois,
expansion of O’Hare International Airport has been the subject of
two such suits.
In State
of Illinois ex
rel.
Scott
v.
Butterfield, No.
74C2440
(N.D.
Ill. 1974),
a group of
municipalities organized as the Suburban O’Hare Commission
(Suburban) participated
in
a suit brought by the Attorney
General.
The allegation was that
the FAA had violated the
National Environmental Policy Act,
42 U.S.C.
4321 et ~q.,
by
adopting
a policy of unlimited growth at O’Hare.
This case did
not come to judgment,
but was the subject of
a consent decree and
settlement agreement dated October 14,
1982
(see Exh.
K,
L; ATA
Brief,
p.
18—19
and Attach
B., and ATA Supp Comments p.
18—20).
Pursuant
to this decree,
among other
things,
the City of Chicago
agreed
to
a moratorium on runway expansion until
1995.
The City
also agreed
to engage in voluntary FAR—iSO planning,
to present
a
master plan
for development
at O’Hare
to the FAA for approval,
and
to request the
FAA
to process an Environmental Impact
Statement
(EIS)
concerning any expansion.
The agreement and
consent decree additionally established
a forum known as the
O’Hare Advisory Commission
(OAC)
for “consideration and
resolution”
of
issues involving the relationship of the City of
Chicago’s O’Hare Airport
to surrounding communities.
On November
14,
1984,
the
FAA
approved an Airport Layout
Plan
for O’Hare which provided
for expansion.
On December
4,
1984, Suburban brought suit against the City and the
FAA
in the
federal District Court
for
the Northern District of Illinois
seeking
an
injunction banning all future construction at
O’Hare.
The complaint was that the FAA’s approval violated the
Butterfield consent decree, NEPA,
the Airway and Airport
Improvement Act of
1982,
49 USC
2201 et. seq.,
and the Clean Air
Act,
42 U.S.C.
7401 et seq.
The district court dismissed the
complaint for lack of jurisdiction.
Suburban O’Hare Commission
v.
Dole,
No. 84C10387, Memorandum Opinion and Order
(N.D.
Ill.
Feb.
28,
1985).
Suburban sought appellate review of the district court order
as well
as the FAA’s approval
of the Airport Layout Plan and the
adequacy of the EIS.
The Seventh Circuit Court of Appeals
determined that Suburban was not legally entitled
to relief.
The
members
of the three—judge panel also stated
that:
we
feel
compelled
to
address
the
equities
of
this
case.
Petitioners
conceive
of
themselves
as
the
innocent, passive victims of a relentlessly expansive
O’Hare.
They point out that many of
the communities
69.81

—18—
surrounding
O’Hare
were
established
long
before
the
airport
had
been
built.
In
all
fairness,
however,
these
same
communities
receive
enormous
economic
benefits
from
their
proximity
to O’Hare.
Moreover,
many
of
these
communities
have resisted
attempts
by
the
City
to harmonize
their own
land—use regulations
with
the
aviation
activity
at O’Hare.
In
a perfect
world, petitioners would
be able to reap the benefits
of their
location
and still
be able
to sleep without
noise disturbances
at
night.
Unfortunately,
the FAA
and
the
City
are
forced
to operate
in
a world where
even
their
most
carefully
considered
decisions
are
likely
to
adversely
affect
some
people.
We
are
confident that the proposed development represents
an
honest
and
careful
attempt
to
minimize
those
consequences
and
to
accommodate
the
conflicting
interests
in
the
best
possible
manner.
Suburban
O’Hare
Commission
v.
Dole,
No.
85—1073,
slip
op.
at
27
(7th Cir. March
13, 1986).
Finally,
it should also be noted
that in Illinois,
as
elsewhere,
individual homeowners have applied
to the courts for
airport noise
relief using
a variety of
legal theories of
liability,
including inverse condemnation, personal injury,
trespass, and nuisance.
See,
e.g., Bryski
v. City
of Chicago,
No.
83 CH841,
(DuPage County Circuit Court)
(complaint discussed
and included
in A.
G. Comments,
p.
62 and A49—60).
The Board
further notes
that in a recent case,
the California Supreme Court
found
that
a homeowners’
suit alleging
inverse condemnation of
land by,
and continuing nuisance from, airport noise
stated a
proper cause of action
for damages.
Baker
v. Burbank—Glendale—
Pasadena Airport Authority,
39 Cal. 3rd 862, 705 P.2d 866,
(1985), cert. denied
54 U.S.L.W.
3561, 3562 (Feb.25,1986).
Airport Proprietors’ Controls
The quandary of airport proprietors has been the
determination as
to what the
limits of its duties and authorities
are
as landlord,
in relation
to its statutory and constitutional
duties
to avoid actions which are “discriminatory,”
“unreasonable” and
“undue burdens on interstate commerce.”
The Illinois Municipal Code,
Ill. Rev.
Stat.
1985 Ch.
24
11—101—1, provides that municipalities:
may establish and maintain public
airports within or
without
their
corporate limits;
may
operate
any
public
airport
and
may
charge
and
collect
rents,
rates
or
other
compensation
for
any
use
thereof
or
for
any
service
rendered
by
the
municipality
in the operation thereof, provided
that
subject
to the capacity thereof,
the landing field
69-82

—19—
and
landing
strips
shall
be available
to any person,
without
unjust
or
unreasonable discrimination
as
to
services and
charges,
for
landing and take—off by
an
aircraft;
and
may
regulate
the
use
of
such
airports,
the
navigation
of
aircraft
over
such
airports
and
the
approach
of
aircraft
and
their
take—off
from
such
airports.
Chapter
15 1/2,
“Aviation”, provides similar, although not
identical,
authority
to establish,
operate and regulate airports
to various counties, municipal airport authorities,
joint city
county airport commissions, multi—county airport authorities, and
inter—state
airport authorities.
However,
local government’s
regulatory powers are not boundless,
being subject,
for
example,
to limitations imposed by the Illinois Department
of
Transportation as well
as the legislature.
See, ~
Ill.
Rev.
Stat.
1985 Ch.
15 1/2
190,
191.
As the Attorney General
correctly relates,
Caught
between
the
local
communities’
inability
to
act
and
the
FAA
refusal
to
lead
is
the
airport
proprietor.
The
proprietor
in
effect
is
caught
on
both
horns
of
a
dilemma.
First,
he
is
responsible
for
the
noise
impact
caused
by
the airport,
but
the
disclosure
of
the
extent
of
the
impact
may subject
him
to
further
liability.
Disclosure
of
that very
data, however, may well assist
the local community in
addressing
the
impact
and
thereby
lessen
the
proprietor’s
eventual
liability.
Second,
the
proprietor
is
subjected
to
the competing demands
of
the
serving
air
carriers
to
increase operations
and
the
local
communities
to
decrease
noise.
(A.G.
Comments,
at 16).
While
the Illinois courts have not addressed the issue of
the permissible scope of proprietor control of noise, case law
developed
in other jurisdictions gives some indication.
A
governmental proprietor may exercise otherwise preempted police
powers to establish a curfew,
see National Aviation v. City of
~yward,
supra
and may ban certain noisy aircraft from use of
its airport provided
that the decision
to do
so
is made in
a
timely
and reasonable fashion, see British Ai~s
Board v.Port
Authority
of New York (“Concorde I”),
558 F.2d 75
(2nd Cir.
1977);
on remand, 564 F.2d 1002 (“Concorde
II”)
(2nd Cir.
1977).
However,
a proprietor may not require compliance with
FAA
regulations
in advance
of FAA’s own compliance timetable because
of
federal preemption of this regulatory area;
see Global
International Airways Co~p~.v. Port Authority of New York,
564
F.
Supp.
795 (S.D.N.Y.
1983).
69.83

—20—
Preemption As Affecting Board Regulatory Authority
Having established the context
of the ATA’s
legal arguments,
the Board may now proceed
to address
them.
This Opinion has
considered
the
FAA’S
disinclination to regulate
airport,
as
opposed
to aircraft noise,
the inability of local governments to
exercise what police and zoning authorities they may possess
to
the satisfaction of themselves as well
as their neighbors, and
the competing and often conflicting federal, local and commercial
interests which airport operators must attempt
to satisfy.
The
argument becomes compelling that state governments could serve
the much needed function of establishing noise limits and
enforcing coordination of efforts between proprietors and units
of local government.
In considering
the possible role of the
state,
the
issues obviously become:
to what extent
is state
action preempted by federal
law, and to what extent is
contemplated state action precluded
by other constitutional
and/or state
law requirements.
As
to the preemption
issue,
the Attorney General and the ATA
do not dispute that the most relevant federal cases are Burbank,
supra, Air Transport Assn.
v. Crotti,
supra, and San Diego
Unified Port District
v.
Gianturco,
651 F,2d 1306
(9th Cir.
1981),
cert den. sub.
norn.
Department of Tran~portationv.
San
Die9o Unified Port District,
455 U.S.
1000
(1982).
The ATA believes that Burbank, as echoed
in the First
District Illinois Appellate Court’s decision
in Bensenville
in
1972 and Priester
in
1974, establishes total preemption of police
power action by state
and local governments
(see ATA Brief,
p.
23—24,
30—31).
The
Board
rejects
this
simplistic
assertion.
To
the extent that Bensenville and Priester
involved
attempts
by
non—proprietors
to exert controls over airport operations and
aircraft,
these decisions correctly noted
the total preemption
principle enunciated by the Burbank court in
a similar factual
situation.
Extension of these holdings beyond
their
facts would
be
error,
in that neither
Illinois court considered,
or was asked
to consider,
the Burbank
footnote
14 proprietor’s exemption now
well recognized by the federal courts and actively embraced by
the FAA.
The prototype for
the Attorney General’s regulatory proposal
to the Board are noise regulations adopted
by the State of
California.
These
regulations have been considered and
interpreted by federal courts
in the Crotti and Gianturco
cases.
In Crotti,
a three—judge district court was designated
to
review airport noise regulations which sought
to reduce community
exposure
to aircraft noise.
These regulations governed the
operations of airports and of aircraft at all airports
in
California mandatorily operating under
a permit
issued by that
state.
The county
in which the airport was situated was given
the responsibility of enforcing the noise regulations.
Any
airport’s non—compliance with the regulations would subject
it to
revocation
or suspension
of its permit.
69.84

—21—
The regulations were written to control noise
in two ways.
Generally, one part of the regulations was designed to gradually
reduce noise
levels
in communities surrounding an airport
to 65
dB under
a metric denominated
as the Community Noise Equivalent
Level
(CNEL).
Certain recommended procedures were established
under
this part of the regulations
to attain the CNEL standards,
such as encouraging
the use of aircraft types with low noise
level characteristics, preferential runway usage, reduction of
flight frequency during noise sensitive periods, noise—shielding
berms, and development of compatible land uses within noise
impact boundaries.
No recommended procedure was mandatory,
and
each airport was left to choose any procedure at its discretion,
including those beyond what was suggested,
in tailoring its own
programs.
A variance procedure was also provided for those
unable
to meet the required noise levels,
and in certain
instances airports with noise problems were required to establish
a Noise Impact Boundary by monitoring and measuring aircraft
noise emissions.
The other part
of the regulations established Single Event
Noise Exposure Levels (SENEL).
The SENEL set out permissible
noise levels governing noise generated by an aircraft directly
engaged
in flight.
Both the CNEL and SENEL standards were
challenged on the basis of preemption, with each party relying on
the Burbank decision
in support of their
respective positions.
After analyzing Burbank, the court first addressed the CNEL
standards.
Here,
the court readily concluded that the proprietor
exemption contained in footnote
14
of Burbank firmly established
the right of the airport proprietor
to control the use of its
airport.
Such control
included the right of the proprietor
to
determine the type of air service provided as well as the type of
aircraft that could utilize the airport.
Further,
the court
specifically recognized that the proprietor’s control could be
exercised either through its own initiative or
through a
directive initiated by the state through its police powers.
389
F.Supp.
at 64.
Moreover,
the court noted
the power of the state
to generally regulate its political subdivisions, including local
airport authorities,
as being
“well established
as a matter of
law”
citing City of Trenton v.
State of New Jersiy,
262 U.S.
182,
185—187,
43 S.Ct.
534
(1923).
389 F.Supp.
at 64,
n.2.
The court also determined that the monitoring provisions
of
CNEL standards were “innocuous
to air traffic involving ground
noise measuring machines and recording sound volume data which
in
no way intrude upon or affect flight operations and air space
management in commerce.”
389 F.Supp.
at 64—65.
Further,
the
state—dictated employment of shielding and ground level facility
configurations, and the development of compatible land uses, were
found as
“so patently within local police power control and
beyond
the intent of Congress in the federal legislation that
further discussion would be wasteful.”
389 F.Supp.
at 65.
69.85

—22—
As the court was reviewing the noise regulations pursuant
to
a summary judgment motion, however,
the court did not decide the
issue of what limits,
if any,
applied
to any of the CNEL
requirements.
Remarking that while
the remaining CNEL
recommended procedures
“appeared
suspect” until such time as
an airport took
a definite affirmative action thereunder, the
court concluded that the CNEL regulations were not per
se invalid
as preempted.
Id.
However,
the court did find that the SENEL regulations
constituted a per
se unlawful exercise of police power into the
exclusive federal domain of control over aircraft flights and
operations,
and airspace management and utilization
in interstate
and foreign commerce.
The court therefore enjoined their
implementation and enforcement
as having been preempted.
Id.
In Gianturco,
the court was subsequently called upon to
review
the implementation of the California CNEL regulations.
The San Diego Unified Port District,
a political subdivision of
the State of California,
owned and operated San Diego
International Airport at Lindbergh Field.
Aircraft noise
from
Lindbergh Field impacted the City
of San Diego
to such
a degree
that the Port District, pursuant
to California’s noise
regulations, was required
to seek
a variance from the regulations
from the California Department of Transportation
(Cal Trans).
The Port District sought
its first such variance
in 1975.
At
that time the Port District voluntarily imposed
a curfew on
operations
at the airport between the hours of midnight and 6:00
a.m.
In effect,
the curfew prohibited any aircraft from taking
off during
those hours and barred any aircraft not certified
under FAR Part 36 from landing during that period.
Subsequently,
the variance was granted, with the curfew incorporated
as
a
condition of the variance.
In January 1977,
the Port District reapplied for
a
variance.
After
a hearing, Cal Trans granted the variance, but
as
a condition thereof,
required that the curfew be extended two
hours,
i.e.,
from 11:00
p.m.
to 7:00 a.m.
The Port District
objected
to the extension of
the curfew,
and challenged
the
condition
in the federal district court, which found
the
condition to
be preempted by
federal law and enjoined
its
enforcement.
Upon review by the appellate court, Cal Trans submitted two
arguments.
The first was that Burbank was
no longer good law.
The basis for
this argument was Congress’ passage
of
the Quiet
Communities Act
of
1978,
Pub.
L.
95—609, which amended the Noise
Control Act of 1978
to establish
a federal program for funding
of
noise abatement plans
for sources including airports.
The court
rejected Cal Trans’
“attempt
to interpret the Quiet Communities
Act as
a blank
check for
local control of aviation noise”
651
F.Supp.
at
1314.
Finding that
the preemption doctrine as
articulated
in Burbank controlled,
the court found that
a local
government
could not adopt regulations impinging on aircraft
69-86

—23—
operation.
The court,
however, took care to mention that its
results were consistent with Crotti.
The court found that the
CNEL regulations upheld
by the Crotti court:
permitted proprietors
to choose
a variety
of methods
to
reduce
noise.
Although
a
curfew was one
option,
it
was
not
specifically
mandated
as
it
has
been
here.
footnote
25.
The
Crotti
court stated that
efforts
to
impose
curfews
via
the
state’s
police
power might be suspect but,
since
the program did not
unambiguously require
this,
it
refrained from
ruling
on the matter.
Footnote
25.
In
Crotti,
the
state
argued
in
its
brief,
made
a
part
of
the
record
in
this case,
that
the
regulations were
not mandatory
upon proprietors,
but only suggestive.
As the state put
it,
Should
a
proprietor
chose
to
act
using
its
unpreemptive
powers...that
is the business of the proprietor.
The
state
has nowhere directed
that proprietary power
be
used.
651 F.2d.
at 1316
Finally,
the court turned
to footnote
2
in Crotti, which
observed that the power of a state
to regulate its subdivisions
was well established.
This power, however, was thought by the
Gianturco court
to be limited through preemption,
referencing
without further discussion the dicta discussed above.
Id.
Cal Trans’
second argument was
that it was
a proprietor of
Lindbergh Field within the meaning of Burbank, and could
thus
impose
the curfew pursuant to the footnote 14 proprietor’s
exemption.
The court disagreed.
Citing Griggs
v. Allegheny
County,
supra,
the court found that for the purposes of
constitutional liability
for
unjust taking of property as well
as
for establishing proprietorship under Burbank,
the criteria to be
assessed are ownership, operation, promotion, and the ability
to
acquire necessary approach easements.
The court determined
that
under
state
law,
it was the Port Authority which satisfied these
criteria and therefore was the airport proprietor.
The concept
of
a dual proprietorship was similarly rejected on state
statutory grounds.
The position of the ATA
is that Gianturco is “fatally
dispositive”
of the Attorney General’s regulatory proposal,
because “Illinois public airport authorities have been ceded
proprietary powers by the Illinois General Assembly identical
in
all significant respects
to the powers held by their California
counterparts”,
as well
as the substantially identical prohibition
against acquisition
of airports from political subdivisions
without their consent (ATA Brief,
p.
26—28).
The ATA asserts
that the Attorney General has conceded
as much,
citing
a
statement made
in the Attorney General’s amicus brief
in support
of Cal Trans’ petition to the Supreme Court
for certiorari:
69-87

—24—
The
Illinois
R77—4
proposal...
applicable
to
all
public
airports
in
Illinois,
would
impose
specific
noise
limitations
for
airport operations as
a whole,
with enforcement and variance mechanisms,
all similar
to
the
California
scheme....The
Court
of
Appeals
decision places
a
large cloud
on the efficacy
of
the
proposal,
and
if
allowed
to
stand
could
render
nugatory
the
entire
regulatory
scheme.
(Exhibit
J,
ATA Brief
at
29).
The argument of the Attorney General
is essentially twofold:
that Crotti has continued validity, and that Gianturco wrongly
decided that the state did not stand
in
a proprietary capacity.
In analyzing these cases,
the Board has not considered
arguments
that the controlling
cases were wrongly decided,
employing instead principles of case construction and stare
decisis.
The Board
finds that Gianturco does not overrule or
otherwise disturb the finding
in Crotti that CNEL standards,
properly applied,
may form the basis
for
a valid state
regulatory
program.
Applying the reasoning of Gianturco,
the Board does not
find that Illinois
is
a proprietor within the meaning of Griggs
and Burbank
Illinois,
therefore, may not dictate what
proprietary controls an airport may
impose.
In terms of the continuum of state action envisioned by the
Attorney General,
this result does not affect the State’s ability
to require “disclosure” and “planning”,
but does circumscribe the
“intervention” options.
The Board’s
ability
to
a)
issue a
general cease and desist order,
leaving a proprietor
to devise
its own compliance plan,
or
b)
to deny
a variance,
leaving
a
proprietor
to adopt
a revised compliance plan,
remains
unaffected;
the range of specific directives may,
however, be
limited.
While
this result may have some undesirable effects,
the
Board notes that
it severely undercuts one of the ATA’s primary
arguments against adoption of
airport noise regulations:
violation of the interstate commerce clause (ATA Brief,
p. 46—
53).
As earlier explained,
the commerce clause prohibits
a state
from adopting legislation or
regulations which places
a burden on
interstate commerce which
is excessive
in relation to the local
benefits which
the state hopes
to achieve.
The essence of the
ATA’s argument
is that any control
of airport noise unduly
burdens commerce,
because of the interconnection of the air
transportation system:
for
instance,
a 10:00 p.m.—7:00 a.m.
curfew at O’Hare,
in combination with
a similar curfew in Los
Angeles,
would prohibit Los—Angeles—Chicago flight departures
for
fourteen and one—half hours out of 24.
Id.
at 51—52.
Uniformity
of regulations
is needed, ATA asserts, and the FAA
is the entity
in the best position to
insure uniformity.
The regulatory scheme proposed by the Attorney General
states the noise levels
to be achieved, not the method of their
achievement.
The airport proprietor
itself must determine the
69.88

—25—
method
of achievement.
This process will inevitably involve
consultation with the FAA, which can assess the effect of any
operational changes on
the air transportation system.
Where
the
FAA does not agree
to operational changes because of their undue
effects on commerce, and
a proprietor cannot achieve full
compliance with the noise limitation,
the proprietor may resort
to the mechanisms for relief provided
for
in the Illinois
Environmental Protection Act,
Ill. Rev. Stat.
1985,
ch.
111 1/2
pars.
1001 et
seq.
(hereinafter
“Act”): variances,
site specific
rules,
or
adjusted standards.
Any burdens
on interstate commerce
may thereby be minimized.
In summary,
the Board finds
that neither
the supremacy nor
the commerce clause preempts the Board from regulating airport
noise
in the manner
suggested by the Attorney General.
State Statutes As Affecting Board Regulatory Authority
Having disposed of the ATA’s federal
law objections, the
Board
will proceed
to consider ATA’s assertion that state
statutes preclude Board regulation of airport noise.
The ATA’s
state law claims
are that the Board lacks general
authority under
the Act
to regulate airport noise,
that
furthermore such regulation would be
in conflict with Illinois
aviation statutes,
that regulation of public airports
(those
operated by governmental entities) to the exclusion of private
airports violates equal protection guarantees of
the state and
federal constitutions, and that the proposed regulations are not
economically reasonable
or technically
feasible.
Title VI of the Act, “Noise”, provides
in pertinent part:
TITLE VI:
NOISE
Section
23
The
General
Assembly
finds
that
excessive
noise
endangers
physical
and
emotional
health
and well-
being,
interferes
with
legitimate
business
and
recreational
activities,
increases
construction
costs,
depresses property values,
offends the senses,
creates
public
nuisances,
and
in
other
respects
reduces the quality of our environment.
It
is
the
purpose
of
this
Title
to
prevent
noise
which creates a public nuisance.
Section 24
No
person
shall
emit
beyond
the
boundaries
of
his
property any noise
that unreasonably
interferes with
the enjoyment of
life or with any lawful
business or
69.89

—26—
activity,
so as
to violate any regulation or standard
adopted by the Board
under this Act.
Section
25
The
Board,
pursuant
to
the procedures
prescribed
in
Title
VII
of
this
Act,
may
adopt
regulations
prescribing limitations
on noise emissions beyond
the
boundaries
of
the
property
of
any
person
and
prescribing
requirements
and standards for equipment
and
procedures
for
monitoring
noise
and
the
collection,
reporting and retention of data resulting
from such monitoring.
The
Board
shall,
by
regulations
under
this Section,
categorize
the
types
and
sources
of
noise
emissions
that
unreasonably
interfere
with
the
enjoyment
of
life,
or with any
lawful
business,
or
activity,
and
shall
prescribe
for
each
such
category
the
maximum
permissible
limits
on
such
noise
emissions.
The
Board
shall
secure
the co—operation
of
the
Illinois
Institute on Environmental Quality
in determining the
categories
of
noise
emission
and
the
technological
and economic feasibility of such noise level
limits.
In
establishing
such
limits,
the
Board,
in
addition
to considering
those factors
set forth
in Section
27
of
this
Act,
shall
consider
the
adverse
ecological
effects
on
and
interference
with
the
enjoyment
of
natural,
scenic,
wilderness
or
other
outdoor
recreational
areas,
parks,
and forests
occasioned
by
noise
emissions
from
automotive,
mechanical,
and
other
sources
and
may
establish
lower
permissible
noise
levels
applicable
to
sources
in
such
outdoor
recreational uses....
For purposes
of
this Section and Section
24,
“beyond
the
boundaries
of
his
property”
or
“beyond
the
boundaries
of
the
property
of
any
person”
includes
personal
property
as
well
as
real
property.
(Ill.
Rev.
Stat.
1985,
ch.
111
1/2,
pars.
1023,
1024,
1025.)
First,
the ATA argues that Section
25 of
the Environmental
Protection Act
is not “sufficiently definitive or specific” to
empower the Board
to adopt
the wide—ranging regulations sought by
the Attorney General.
ATA asserts that Section
25
is a general
grant of authority to
“adopt regulations prescribing limitations
on noise emissions beyond the boundaries of the property of any
person”,
as opposed to a specific mandate to regulate airport
noise as enacted,
for
instance,
by the California legislature
as
discussed
in Crotti and Gianturco.
The ATA also asserts that
airport noise regulation
falls outside the scope of the
permissive authority of
Section
25 to the extent that the
69-90

—27—
proposal would cover
a)
noise emitted by aircraft while
operating miles outside the airport’s boundary, and
b)
the
“property” emitting the noise——the aircraft——is not owned by the
airport.
Initially,
the Board must point out that the second
paragraph of Section
25 specifically mandates the Board to
categorize “unreasonably interfering” noise
sources and to
prescribe noise
limits.
The lack of
a legislative “laundry list”
identifying particular noise sources, such as airport
noise,
as
being subjects of special concern does not impair the general
grant of
regulatory authority.
Section
25
is both definite and
specific, particularly when
read in the context of the Title
as a
whole.
In support
of
its
argument that the Board cannot
“limit the
aggregation of noise caused
by aircraft operating miles beyond
the boundaries
of the airport”
(ATA Brief, Oct.
26,
1983 at 59),
the ATA cites the following language from
In The Matter
of
Proposed Noise Regulations
for Toys,
R72—l6,
6 PCB 131
(October
31,
1972):
It
will
be
seen
from
the
above—quoted
provisions
Sections
23—25
of
the
Act
that
the
Board’s
jurisdiction
for
the
adoption
of
regulations
in this
field
related
to noise emitted
beyond the boundaries
of
the
property
on
which
the
noise
has
been
generated... (emphasis added).
Reliance
on this incomplete quotation
is badly misplaced.
The
toy noise proposal was
to impose
a 100 dB limit on noise from toy
guns and
an
85 dB limit on noise from other
toys measured one
foot from the
toy.
The sentence following that quoted above
contains
the essence of the Board’s rationale for dismissing the
petition:
The
proposed
regulation
is
essentially
one
in
the
category
of
consumer
protection
and
does
not
fall
within
the
area
of
control
envisioned
by
the
Legislature
for
which
the
Board
is
authorized
to
enact regulations.
Furthermore, Professor David Currie,
the principal draftsman
of
the Act, has stated that the “beyond the boundaries”
language
of Section
25 of the Act “excludes industrial hygiene,
as
in the
previous air statutes;
meaning
that
the Board has shown no
inclination
to duplicate the work
of other agencies
in
indoor
air
pollution.”
Currie, Pollution at 123
(1975).
Thus, the Board
has not attempted to regulate noise, such as toy noise, which
does not generally escape the boundaries
of the property on which
it
is generated.
The Board
has, however,
adopted regulations
limiting noise emissions from mobile sources on roadways
R74—lO,
25 PCB 517, 641, Order May
12,
1977,
since mobile source noise
reaches and impacts the general environment.
69-91

—28—
Next,
the ATA argues that
“the proposed regulation purports
to target Illinois public airport proprietors even though the
entities do not own the property,
i.e.,
the aircraft, which are
the source
of the noise being emitted”, and that the regulations
adopt
the “guise of
regulating
the airport proprietor
in order
to
reach
the source of the noise
itself,
i.e.,
the aircraft in
flight”
(ATA Brief, Oct. 26,
1983,
at 60).
However, while the
noise
is generated
by the aircraft,
the impact of that noise
depends upon the location of the airport property,
its size and
configuration,
the flight paths (especially during take—offs and
landings),
the timing
of arrivals and departures, airport
operating procedures,
surrounding
land uses, and other factors,
many of which are under
the control
of the airport proprietor.
As the Attorney General has pointed out,
“just as
planes
do
not wander about
in the sky like vagrant clouds’
(quoting
Burbank, 411 U.S.
at
633, planes likewise do not take—off and
arrive
(with
their indivisible noise)
on vagrant clouds,
but at
proprietor located and controlled airports”
(A.G.
Reply Comments,
Nov.
28,
1983 at 19).
Clearly,
the airport proprietor’s original decisions
as to
airport location, configuration and design,
as well
as ongoing
decisions regarding new construction, operating procedures and
additional
land or easement purchases have
a real effect upon
airport noise
impact.
The Supreme Court,
in the context of an
air easement case,
recognized this fact:
It
is
argued
that
though
there
was
a
“taking”,
someone
other
than
the
airport proprietor
was
the
taker
——
the
airlines
or
the
C.A.A.
acting
as
an
authorized
representative
of
the United
States.
We
think,
however,
that
the
proprietor
,
which was
the
promoter,
owner,
and
lessor
of
the
airport,
was
in
these circumstances the one who took the air easement
in
the
constitutional
sense.
The
proprietor
decided,
subject to approval of
the
C.A..A., where
the
airport would
be
built,
what
runways
it
would
need,
their
direction
and
length,
and
what
land
and
navigational easements would be needed.
Griggs supra,
369 U.S.
at 89
(1962).
The rationale used by the Supreme Court here,
that the
responsibility for a taking accrues
to the decisionmaking entity,
is one which
the Board has long and consistently applied
in
analyzing liability for pollution under the Environmental
Protection Act:
The
Act
makes
it
unlawful
not
only to
‘cause’
but
also
to
‘al1ow~~o11ution. We
think
this
language
goes beyond
the common law arid imposes an affirmative
duty on persons in
a position of potential control
to
take
action
to
prevent
pollution.
.
.
the question
for
our decision
is whether,
in light
of the
Act’s
policy,
a respondent
is
in such
a relationship
to the
69-92

—29—
transaction
that
it
is
reasonable
to
expect
him
to
exercise control to prevent pollution.
EPA
v.
James McHugh
Construction
Co.,.
PCB
71—29,
4
PCB 511,
513
(May 17, 1972).
See also,
EPA v. Village
of Millstadt, PCB 78—132,
31 PCB 391
(Sept.
7,
1978)
(“The Act prohibits any person
(including
corporations) from causing or allowing
a violation of the
regulation,
regardless of whether such violation was caused or
allowed as
a result of
a contractual arrangement”); EPA
v.
Meadowlark Farms,
Inc.,
6 PCB 537
(PCB 72—343, January 16,
1973)
(“We are not concerned with the refinements of ownership of the
source
of pollution
as much
as with the capacity of controlling
its pollutional discharge.
Respondents cannot be selective about
what aspects of the
source
are under
its control.
The burdens
must be accepted with the benefits”),
affirmed, Meadowlark
Farms,
Inc.
v.
Pollution Control Board,
17 Ill.App.3d 51,
861
(5th Dist.
1974).
Thus,
the Board
finds that regulation of airport noise,
provided such regulation
is accomplished in
a constitutionally
permissible manner,
is both authorized by the Act and necessary
to implement the purposes of Title VII.
The ATA’s assertion of conflict between aviation statutes
and noise regulations promulgated under
the Act can be dismissed
with
little discussion.
The ATA contends that the aviation
statutes authorizing municipalities
(Ill.
Rev. Stat.
1985,
ch.
24,
11—101—1, previously quoted at length) and other
governmental entities
(Ill. Rev.
Stat.
ch.
15 1/2 generally, and
specifically
187—194)
to operate airports require them to
provide unlimited access
to all persons.
ATA asserts that
airport noise regulation would prevent compliance with this
requirement,
based on language prohibiting “unjust or
unreasonable discrimination.”
The statutes do not preclude
“reasonable discrimination”
for purposes of noise abatement;
the
statutes
in fact go on
to provide for regulation of the use of
the airport and the aircraft’s navigation,
take—off and
approaches.
However,
Section 47(a)
of the Act requires that the
“State
of
Illinois and all its
...
subdivisions shall comply with all
provisions
of the Act and of regulations adopted
thereunder.”
Compliance with an airport noise regulation
presents no inherent conflict with the aviation statutes
authorizing
regulation of airports
in a “just”
and “reasonable”
fashion.
The final argument of the ATA concerns the proposed
regulation of noise from public airports only.
The first noise
regulations, adopted
in Docket R72—2,
were challenged
on similar
grounds.
The validity of these regulation was upheld in Illinois
Coal Operators Assn.
v.
PCB,
59
Ill.
2d
305,
319 N.E.2d 782
69.93

—30—
(1974).
One of many areas
of challenge was the exemption of
sounds emitted by construction equipment from the regulations,
when identical equipment used
in mining was not also given an
exemption.
It was argued that this differing treatment violated
the equal protection clauses
of the state and federal
constitutions, as well as
a state prohibition against special
legislation.
The Illinois Supreme Court cited numerous authorities
which
specify groundrules to
be used by the legislature
in creating
classifications for differing treatment; these apply to the Board
in its use of
its quasi—legislative powers of rulemaking:
We
would
remark
that
so
far
as
legislative
classification
is
concerned,
it
has
been
recognized
that
evils
in
the
same
field
may
be
of
different
dimensions
and
reform
may
take
place
one
step
at
a
time.
The
legislature
may
address
itself
to
one
stage
of
a
problem
and
not
take action
at
the
same
time
as
to
other
phases.”
319
N.E.2d
at
786
(citations
omitted).
....If
there
is
a
reasonable
basis
for differentiating between
the
class
to which
the
law
is
applicable
and
the
class
to which
it
is
not,
the
General
Assembly
may
constitutionally
classify
persons
and
objects
for
the
purpose
of
legislative
regulation
or
control,
and may pass laws
applicable
only
to
such
persons
or
objects.
319
N.E.2d at 785
(citations omitted).
In that case,
the court found that there were significant bases
in the
record
for distinguishing between the mining and
construction industries,
including the temporary vs. permanent
use
of equipment, the different areas of
the state
in which the
activities were primarily conducted, and the number of persons
employed.
Similarly,
the Board
finds that this record supports a
rational distinction between public and private airports.
As
enunciated
by the Attorney General:
Privately owned airports are
a different contaminant
source from those
owned by public entities.
They are
typically
much
smaller
and
more
isolated;
and
their
operations
are
dominated
by
general
aviation
and
fixed—based aircraft whose operating needs
and noise
characteristics
are
altogether
different
from
the
scheduled
commercial
jet
airliners
which
dominate
operations
at
airports
operated
by
public
entities.
(Amended proposal
of 6—12—73, Rule 501
“Purpose”).
Additionally, political subdivisions are vested with
explicit statutory authority to
regulate their airports, which
authority may arguably give them greater noise abatement powers
than non—governmental airport proprietors possess.
Additionally,
69-94

—31—
state government has an obligation
“to manage its activities
so
as
to minimize environmental damage.”
Ill. Rev. Stat.
1985 ch.
111 1/2,
par. l002(a)(4).
For
these reasons, the Board
finds
that
it may lawfully address
itself first to the noise problems
posed
by political subdivisions of the state over which the power
to regulate
is well established.
E.g.,
City of Trenton
v.State
of New Jersey, 262 U.S.
182
(1982).
The only legal challenge remaining concerns the economic
reasonableness
and technical feasibility of
regulations
to
be
adopted by the Board.
This can be answered only after
a detailed
examination of
the record
in this proceeding.
CITIZEN CONCERNS
Many persons impacted by airport noise appeared at the
Board’s hearings and testified about
its effect on their lives.
A small fraction of those
comments will be quoted
or referred
to
in this opinion.
Frequency
of Flights
While noise levels are attributable to
a number
of
variables,
the frequency of flights was
of great concern
to
residents around
the Chicago airports.
With 731,742 operations
(landings or takeoffs) per year, O’Hare has 2,000 operations
a
day or
an
average of
83 per hou~. One Elmhurst citizen testified
that depending on wind direction,
landings occur every 75 seconds
and
takeoffs occur every 50 seconds
at O’Hare runways 4R and 22L
(R. 655).
A second Elrnhurst citizen said that planes land at
runway 4R every 15—20 seconds
(R. 687, 690—1).
A third stated
that unbearable noise
from runways 22L and 4R occurs every 50
seconds for 14 hours on
a northeast wind day
(R.
742).
A Des
Plaines resident testified that noise from planes using runway 22
is
continuous
from 7:30 a.m.
to 9:30 p.m.
(R.
992).
Another Des
Plaines homeowner stated that approximately 90,000 planes fly
over his home per year at
an altitude of less than 400
feet.
Impact of Noise on Peopie’s Lives
Many citizens testified that they could not enjoy
the use of
their homes or property because of the airport noise.
These
complaints can be categorized as communication interference.
Indoor communication interference occurs when the noise
interferes with
the resident’s ability to hear
the television,
stereo,
radio,
telephone,
or each other, which happens
in many
suburbs of O’Hare including Glenview
(R.
1008), Elmhurst
(R.
366,
718),
Schiller Park
(R.
711),
Des Plaines
(R. 2968,
2976,
1039—
42) and Bensenville
(R.
425).
A Bensenville resident summed up
the indoor communication interference
as follows:
It
is
impossible
at
times
to
carry
on
normal
conversations
in
a
variety
of
situations.
Sitting
69.95

—32—
outside
on
our
patio
we
are
frequently
unable
to
carry
on uninterrupted discussion.
Inside our home,
on days when we do not have the
air conditioning on,
the noise
interferes with our mealtime
banter.
When
using
the
phone
we
frequently
must
stop
talking
because
of
the roar of plane, and
if we happen
to
be
speaking to someone here
in Bensenville who is
in the
path
of
the
same
flight
pattern
the conversation
is
interrupted
two
times,
once
as
the
roar
is
at
our
house and then at their home, and also with each take
off during
the conversation
ER.
425.
Indoor communication interference problems extend to
hospitals and schools.
A registered
nurse at Lutheran General
testified that:
While
working,
I
have seen
how patients respond
to
noise pollution
from planes going
in
for landings
at
O’Hare.
It
appears
the
patients
do
become
more
irritable
and
nervous
when
noisy
aircraft
are
heard.
The
noise
interrupts
conversation
,
not
to
mention the patients’ experience when trying
to
rest.
It’s
important
to
have
quiet
when one
is
doing
certain procedures such as taking blood pressures and
this
is
interrupted
by
the
noise
from aircraft
ER.
4241.
Airport noise also interrupts church services.
The pastor
of Our Lady of All Parish
in Roseniont testified that:
In
terms
of
giving
homilies
on
Sunday,
things
like
that,
it’s
very
difficult.
There
are certain
days when we have
a northeast wind and we just know,
the
parishioners
know
we
have
to
cut
the
homilies
short.
There
is no way we can really communicate
to the
people.
It’s nearly wiped out of existence on those
days.
Other times,
it’s not that bad
ER.
4236.
A Bensenville resident testified that:
We go
to church
services and
all
throughout
the
service
we
have
to
hesitate.
Sermons
have
to
be
stopped because
of the noise of
the aircraft.
At any
rate,
it
is
very
discouraging
and
certainly
disrupting
to
the message being given during
sermons
and services.
ER.
5842).
Complaints
of airport noise extend even
to the sports
arena.
A witness attended
a football game that was stopped eight
times
by
the
referee due
to aircraft noise
ER.
404).
A school
superintendent stated
that:
69-96

—33—
that...is
the
way
we
play
our
football;
the
quarterback puts his hands
up, we wait
‘til the plane
passes over,
and we run the play.
I think
it
is safe
to say from impartial research that we spend
20
to 30
seconds for each pass over.
ER.
290.
One elementary teacher at
a school which
sits under runway
22R, testified about the problem:
The
first
problem
that
we
have
deals
with
spelling.
Whenever
the words
are given the children
will
raise
their
hands
and
point
overhead,
which
means
I can’t hear you,
there
is a jet overhead.
And
I have
five classes
of
language arts,
which
means
on
certain days we have
to
stop five
to
twenty
minutes
in each class, this
is
in spelling...
In
reading
it
is
impossible
to
present
a
new
word
on
the
board
as
a plane
is
going
overhead.
We
have groups of children coming up and saying,
‘We can
see
the
board
but
we
can’t
pronounce
the
word.’....And
I
notice
as
I
have
been
teaching
in
Park
Ridge
the
increase
in
noise
level
is
getting
worse and the frequency is increasing
ER.
392—3.
The superintendent of the school district testified that
O’Hare runway
22L,
22R and 27R operations fly over six of
the
district’s schools and affect five others
(R. 387).
Even when schools are air conditioned complaints exist.
The
Superintendent of Bensenville School Districts
2 and 100
testified that:
I
submit
to
you
that
air
conditioning
is
a
wonderful
thing
and we’re
all enjoying
it today,
but
in
the
fall and spring boys and girls
in our schools
can’t
enjoy
air
conditioning,
they can’t
even
enjoy
open
windows
because
of
noise
pollution.
The
only
defense
we
have
against
noise
pollution
is
the
windows
R.
287
People have testified that they have had difficulty sleeping
because of airport noise.
A Mount Prospect resident stated:
I
did
not
get
any
sleep that day,
nor
did many
of my neighbors get much sleep.
I am
——
I
feel that
is excessive.
I
feel
it
is excessive
that
I
have
to
be subject
to
22 straight hours of noise.
I
think
it
is
excessive
that
my children
can’t
go
to
sleep
and
therefore cannot go
to school
the next morning and be
educated.
I
think
it
is excessive that
I
cannot go
to work
the next day and earn a living
for my family,
69-97

—34—
and therefore
I am concerned
R.
267
A Bensenville resident also testified:
Let
me
get
back
to
my
typical
day
in
Bensenville.
Okay.
I will
be
sleeping
in my bed at
3:00
o’clock,
ten
to
3:00
a.m.,
charter
flights
to
Europe,
everybody
knows
them
because
you
can
get
a
good deal
on
it,
there
are
at
least
sic
flights
at
night.
When
they
land
——
I
am
sorry,
take off over
the house at five
to 3:00,
ten to 3:00,
3:00 o’clock,.
I will get up every morning
to look at the clock, and
then
I
try
to
get
back
to
sleep.
My
bed
is
shaking.
I
kid you not,
it vibrates,....
R.
401-
02
.
A Des Plaines resident stated:
This morning
I
opened
my
back
door and
I
said,
‘good
morning
airplanes’,
because
they
were
back
again.
You
go
to
sleep
with
them.
You wake
with
them.
I have
a four—year old who
I can’t even put
to
bed at 8:00 o’clock at night because she says,
‘Could
you please stop the airplanes?’
R.
2976—77
Airport noise also interferes with outside communication.
One Schiller Park woman complained
as follows:
We can’t stand out in the yard.
You can’t
talk
on
the
telephone.
You have
got
to
be
closed
up
all
summer
arid you call that right.
They
should
have
all
the
right,
and
I
have
to
sit
in
my house all
summer.
I
think
it
is
terrible
in
this
day
and
age
we
should
have
to
put
up
with
such garbage.
And
if
I was
to
sell my
house,
I
wouldn’t even
be able
to sell
it.
I wouldn’t want somebody else
to
go through what
I go through.
Something
should
be done
and
something could
be
done....You
want
to
wait
‘til
we
all
get
a
nervous
breakdown.
I
am
just
about
at
it.
They should
pay
me
for what
I am going
through
ER.
711—12.
Similarly,
an
Elmhurst
resident
was
disgruntled
over
the
impact
of
the
airport
noise
on
the
ability
of
residents
to
use
the outdoors:
We
had
a
block
party
this year
and
the
noise
bothered
many
of
the
residents
of my
neighborhood.
And
I
recall
it
when
we
were
planning
this
block
party,
we
really
prayed
that
we
would
have
a
nice
69-98

—35—
warm
day,
we
prayed
that
it
wouldn’t
rain,
we
also
prayed
that
the
airplanes
wouldn’t
come
over.
And
that
is
true.
We did talk about
that
R.
704.
A representative of the Bensenville Home Society,
a social
service agency which operates
a 247—bed facility
for
the aged
in
Bensenville, also testified:
We
have
beautiful
grounds
surrounding
the
facilities which are
of
little use
to us
because the
residents
find
the
noise
so
unbearable
most
of
the
time
from
the
aircraft
that
they
prefer
to
remain
indoors.
This is very sad.
I
might
add
that
the Bensenville
Home
Society
has
been
in
existence
in
that
location
since
1894,
long
before
the
airport
was
even
dreamed
about
ER.
5841—2
Airport noise can even interfere with the vital
communication services as evidenced by the testimony of Sergeant
Mosher
of the Bensenville Police Department.
He
testified as
to
the effect of airport noise
on the department’s radio
communication system:
I
have
occasioned
several
times
when
a
total
communication
blackout
occurs
because
of
the
jets
going
over.
Everyone
in
the audience here knows that
frequency
with
which
they
go
over
and
if
you
can
imagine
a
forty—five
second,
thirty
to
forty—five
second
blackout
in
our
communication,
it
becomes
almost
unbelievable
how
we
can communicate
back
and
forth with the frequency with which the jets go over.
We
operate
under
this
on
a
24—hour
basis.
Our
contact
with
the
jets
is
so
close
that
I
have
had
officers
tell
me
that
while
on
York
Road
they
can
clock
the
jets on their
radar units,
it’s that close
to us,
and the noise
is that great
for
us and
it does
cause
a vital problem to us and hampers
us
to a great
extent
in
our
ability
to
serve
the
public
and
the
Village of Bensenville.
ER.
6587.
In addition
to the frustration of being unable
to
communicate indoors or
to enjoy the outdoors,
residents are also
caused discomfort and expense
by noise vibrations.
One woman
from the Mohawk subdivision
in Bensenville testified that
“pollution
is also vibrations,
vibrations that have broken two
bedroom storm windows...vibrations that have cracked the patio
twice....It has also cracked the ceiling.”
(R.
6566).
A man from
the same subdivision testified that planes
from O’Hare pass over
the subdivision homes
at about
150
feet.
“We have been
continually fixing
the ceiling from cracks.”
(R.
6665—6).
Even
the Mohawk School
in Bensenville
vibrates
(R.
298).
A
69-99

—36—
Bensenville woman summed up the vibration problem,
testifying
that:
when
you
sit
at
the
dining
room
and
a
plane goes
over,
my
chandeliers
shake,
the
china
in
the
hutch
shakes
to
the point
that
I put most
of
it underneath
because I’m
afraid
some day
the
chandelier
is going
to fall
on top
of
us
and
the
china
is
going
to come
out....
I mean you can see
the people
in
the planes
practically
looking
down
on
you
and
you
feel
like
they are
staring
or
laughing
at you because you are
foolish
enough
to
live
in
a
home
that you
love
ER.
5864—5.
Others testified that they could not enjoy
the full use of
their home or property
(R. 450, 741, 4360).
One resident of Des
Plaines
stated that
the noise
is so loud
“that
I can’t even tell
if the lawnmower is going.”
(R. 4358).
He stated
that he was
frustrated,
and many times
ends up yelling and getting
irritable.
Id.
Another Des Plaines resident spoke of stress:
The
stress
factor
has
been
great,
as
I
say.
They
are
talking
about
those
hostages,
39
hostages,
or
55
in
Iran,
and
an
entire country
is
willing
to
sacrifice,
but
here we
hav.e
two people
in our
house
who
are hostages
of
the
airlines;
and
I guess
there
are many,
many more,
.
.
.
and
no one
is willing
to
sacrifice for us
ER.
5058).
Others testified as
to the stressful situations caused
by
the noise.
An Elmhurst resident stated:
And
I
also
feel
that
the
rights
of my having
a
home,
that
is,
a
healthy
home
is
being
violated
because
I
do
feel
that
.
.
.
the
noise
hurts
my
ears.
And
I do feel
that
it creates
a great deal
of
tension between myself and my wife and my family.
So,
I
do
believe,
then,
that
our
individual
rights
are
being
violated.
And
I
hope
that
the
Attorney
General’s
office
will
recognize
this
fact
and
will protect
us
because
really we
can’t
protect
ourselves
ER.
765.
Another Elrnhurst resident testified that:
I
am
a
wreck
sometimes.
I
just want
to
get
a
missile
and
shoot
at
every
one
of
those
planes,
at
every one of them.
This
is
emotional
testimony,
but when you’re
in
the situation you do get emotional
ER.
3281.
69-100

—37—
An Elmhurst resident commented on the psychological
impact.
of the noise:
I
only
notice
the
airplanes
on
weekends.
I
don’t notice them during the week, except when
I come
home
from work.
After working
in the Loop
I
return
to my nice lovely home
in quiet tree—lined
streets in
Elmhurst and my wife
is
a miserable bitch, pardon the
French.
She
is
normally
a
very
lovely
woman,
but
after
three
or
four
hours
or
whatever
it
takes
of
airplanes flying over my house is not very nice.
We
talk
about
physiological
health
and
bodily
effects,
and
the
like
but
nobody
talked
about
psychological
welfare.
And
I
think
this
does
more
damage
to
us
psychologically
than
it
does
to
us
physically.
ER. 752)
Things had not improved much by the time of the September
1985 hearings which were attended by far
fewer residents.
A
Chicago resident testified that the Midway Airport noise problem
as he perceives
it began in
“1983 when they started the
expansion.
In 1983,
it was not bad.
But 1984,
it has just been
absolutely terrible”
(S.
43).
Another Chicago resident testified about
recent noise levels
at Midway:
-
I
live
about
a
half
mile
from
Midway
airport
that has
a
large number
of older
DC—9 planes.
These
planes
are very noisy
and fly over low
in and out
of
Midway,
causing
my
windows
to
rattle.
The
mortar
falls
from
the
walls.
You
can’t
hear
on
the
telephone and
it
interferes with
all the TV programs
S.
36—7
Ground Noise
Several witnesses were more concerned about ground noise
than that generated by planes
in flight.
Airport ground noise
results from run—ups, taxiing and aircraft maintenance:
Ground noise begins with
a very loud,
you know,
big
shock
and
runs
for
fifteen
seconds,
twenty
seconds,
thirty
seconds
and
then
shuts
off.
Then
they
will
figure
out
there
is
something
else
that
they
have
got
to
fix
and
do
it
again.
It’s
the
ground noise
of that type that has caused us the most
problems
ER.
4345
One woman testified regarding the intensity of maintenance
run up noise:
69-101

—38—
My husband
and
I were awoken
at approximately
a
quarter
after
twelve
at night.
There was
a terrible
sound
that was
shaking
our
house.
We
did
not
know
what
it
was.
We
thought
at
first
maybe
it
was
a
tornado.
It
was
a
bad
night,
Sunday
night.
There
was
lightning
and
thunder
and
this
sound
just took
over everything
else.
We
tried
to
find
out.
We
called
the
Police
Department
to
see
if
they knew what
the
noise
was;
they knew nothing of
it....
My husband
finally called
the airport and asked
them
if
they
were
testing
some
new
kind
of
run—up
which
he
explained
to
my
husband
is
they
take
the
airplane
to
the
ends
of
the
runway
and
rev
the
engines
as high as
it will go.
My
husband
told
me
——
he
says,
‘Man,
our whole
house
is
shaking.’
The noise
was
unbelievable.
He
says,
‘Well,
it
will
last
about
fifteen
minutes
longer.’
It
lasted
a
least
fifteen
minutes
longer
although
it
did
lessen.
They
must
have
moved
it
either up the runway
or to
a different
runway,
but we
could
still
hear
it and
for anybody that experienced
this,
it’s
really
something.
I
mean,
the noise was
unbelievable and
this was
in
the middle
of
the
night
R.
6661—62)
Another woman testified about the frequency and duration of
ground
noise:
We
used
to
be
able
to
distinguish
rev—ups
because
they
would,
as
they
were
doing
the
other
night,
they would gun
it and shut
if off abruptly and
that
in
itself
jolts
you
out
of
your
bed,
but
they
don’t always do that,
so as
a result,
I can’t tell if
it’s
a
plane
that
is
there waiting
to take
off
or
a
plane
that
has
just
landed
waiting
to
go
to
the
terminal.
.
You see, when you live where we live you get the
noise
of
the
planes
taxiing....Then
you
get
them
coming
over
slowly and
then they go up
and,
I would
venture
to
say,
most
planes
using
those
runways
are
heard
in
our
area maybe
two
or
three minutes,
which
is
a lot when they are, maybe,
five minutes apart....
Q.
Is
the
noise
on
the
ground
more
continuous,
perhaps?
A.
Yes, you would
swear
that
there was
a
plane out
on
Touhy Avenue with
its engine
running
for
a half—
hour, forty—five minutes at
a
time.
69-102

—39—
Q.
For
that reason, does that bother you more?
A.
Well,
yes,
I would
think
it would anybody because
when
a plane
is in
the air and
it goes over and it’s
gone,
you assume
that,
okay, maybe another one won’t
come
over
for
an
hour,
but
when
it’s
on
the ground
and
it’s constant,
obviously,
it
would
be bothersome
to
anyone
who
is
bothered
by
it,
right?
R.
4313—
4318
A Des Plaines
resident, complaining about ground noise
testified:
We
do
hear
other
ground
noise
where,
for
example,
at about 6:00 o’clock
at night there must be
35,
40,
50
flights
that
leave
and you
hear
one
taxi
up
to
the end
of
the
runway and then
roar
it up and
take off and that goes
on ad
infinitum.
R.
4349
Ground noise and run—ups also occur
at other airports such
as at Coles County Airport
(R.
1785) and Springfield
(R.
1711).
The O’Hare situation
is simply more extreme.
Noise Impact on Property Values
The impact of airport noise on property values was
frequently discussed at hearing.
The testimony of individual
property owners differed according
to their location
in relation
to an airport and their personal experiences.
The testimony of
a
realtor and examination
of exhibits provided more detailed
information.
A former resident of
River Forest testified that she sold
her home
in three weeks after deciding
to move because
of noise
related
to
a new runway.
Regarding the sale price
she said,
“We
made money on
it.
But the people didn’t know what they were
getting into.”
(R.
219).
She also said that sales were
“hot”
in
the area due
to its beauty and other amenities.
An Elmhurst
resident said that his property had “gone down in value
considerably”
(R.
691).
A Chicago resident living seven miles
from O’Hare thought that values
had generally gone
up
in his
neighborhood,
but noted that people
in other
areas thought their
values
had declined
(R. June 12,
1978, 3049).
Another woman
said:
At this
time of year,
it’s too hard to sell your
house.
You have
to pay twice
as much if you want to
move
into
a house
the
same
as
the
one
that you
live
in now,
but the noise
is
so horrible
R.
5861.
A Bensenville realtor was
later asked
if
he had suffered
similar effects.
He said:
69-103

—40—
Very specifically,
yes.
And
very
specifically
in the residential
real estate business,
I hear these
constant
complaints
from
my
customers
and
clients.
There
are
areas
of
these
towns
that
are
less
desirable because of the air traffic
R.
5852
The Chairman of the Elk Grove Aviation Committee said:
I
would
imagine
that
most
previous
testimony
hinged
around
the
negative
economic
impact
the
amendment
would
have
on
business
in
the
area.
Has
anyone considered or evaluated the negative impact on
real
estate
values
of
residences.
Many
homes
have
been sold
below market value,
and many
homes
cannot
be
sold
because
of
the
ever—increasing
noise
pollution
R.
5014
General von Kann of the ATA did not think
that property
values had actually declined.
He testified as
follows:
There
certainly
is
little evidence
of decreased
property
values
if
you
look
at
some
of
your
census
tracts and you look
at
such things
as
the value
of
a
median
family
home
in
the
so—called
impacted
area
here compared with what has happened
to the values
in
the non—impacted areas
ER.
3182
Impressive testimony on this issue,
however,
was presented
by
a licensed real estate broke~who has practiced in Des Plaines
for fifteen years.
He holds an instructor’s certificate
in real
estate appraisal from the University
of Minnesota and is a
graduate
of the Realtors’ Institute
arid
a senior member
by
examination of the National Association of Independent Fee
Appraisers.
He served
as President of the Northwest Suburban
Chapter of the National Association of Independent Fee Appraisers
for three years and works for
a firm which has been actively
engaged
in real estate brokerage
in Des Plaines for fifty—two
years.
He testified as follows:
I
wish
to
address
you
concerning
the financial
impact
of
noise
pollution
on
a
residential
neighborhood.
The
impact
of noise pollution is many
faceted
and
it’s
difficult
to
address
in
a
direct
manner.
I
have
chosen
the
residential
neighborhood
located south
of Touhy Avenue, east of Mannheim Road,
west
of River Road and north of the Northwest Tollway
as
an
example
of
a
noise
polluted
area
and
have
compared
this
area
to
the
balance
of
Des
Plaines
north
of
Algonquin
Road.
I
have
omitted
the
area
north
of
Touhy
Avenue
and
south
of
Algonquin
Road
since
this
will
eliminate
the
transition
neighborhoods and provide a clear contrast.
69-104

—41—
My first conclusion drawn in comparing these two
contrasting
areas
of
Des
Plaines
concerns
home
improvements.
I
have
found
that
there
is
a marked
lag
in home improvements directed
to the enjoyment of
outdoor
lifestyle
such
as
screened
porches,
patios
and family room additions
for homes suitable for this
improvement
are
about
one—half
as
frequent
in
the
noise
impacted area.
The
lack
of
patios
and
other
outdoor
improvements would
appear
to
be
an
obvious
reaction
to
noise
pollution
which
we
would
expect,
but
the
lack
of
family
rooms
and
other
substantial
improvements
is
unexpected
and,
in
my
opinion,
ominous.
This
reluctance
to
invest
in
one’s
own
neighborhood
is
a dangerous
factor
which
is normally
found
in
declining
neighborhoods
to
a
much
greater
extent.
I do
not
suggest that South Des Plaines
is
in
a
state
of
decline.
To
the
contrary,
it’s
an
area
which
is
growing
and
improving,
though
at
a
much
slower
rate than other Des Plaines neighborhoods.
In order
to address specific impact of pollution
in
a
dollar
amount,
I
have
selected
the
home
style
which
is
subject
to
the
least
variation.
I
have
compared
only
two
bedroom,
brick
ranches
with
one
bath,
no
basement,
no
family
room,
no
central
air
conditioning,
but
with
a
garage.
I
have
used
the
annual
sales
summary
or
the
northwest
suburban
multiple
listing
system for
data using
1977 and 1978
as
a basis of comparison.
All home
sales
in
the selected areas which meet
this description has
been
included.
There have been
no
omissions.
Within
this
strict
description
there
were four sales in South Des Plaines in 1977 and five
in
1978.
North of Algonquin Road there were eight in
1977 and four in
1978.
Averaging
the
sales
of
1977
and
averaging
the
sales
of 1978,
the pattern
is established.
Homes of
this
modest
description
sold
for
$57,168.50
on
an
average
north
of Algonquin Road;
yet,
the
same home
in
a
pollution
impact
area
sold
for
an
average
of
$53,367.50,
a difference
of $3,801.
It
should
be
kept
in
mind
that
this
figure
is
for
a
modest,
two—bedroom
home
with
few
amenities.
Most of the homes of
the noise impact area are larger
and
these
homes would
suffer
even greater
loss,
but
for
purposes
of
extrapolation
on
an
overly
conservative
basis,
the
approximately
850
homes
69-105

—42—
located
in
this
single
impacted
area
suffer
an
economic
loss well
in
excess
of $3,230,000
ER.
4263—
67.
Additional evidence of the negative
impact of airport noise
on residential property values
is provided in
a 1985 FAA report
entitled Aviation Noise Effects.
A summary of
a number
of
studies was presented.
The range of property value decrease per
decibel above 55 Ldn was given as 0.6 percent
to 2.3 percent of
the property’s value depending upon the city studied.
The report
concluded:
The bottom line
is
that noise has been shown to
decrease the value
of property by only a small amount
——
approximately
1
percent
decrease
per
decibel
(DNL).
At
a minimum,
the depreciation of
a home due
to aircraft noise
is equal
to the cost of moving
to a
new
residence.
Because
there
are many other
factors
that
affect
the
price
and
desirability
of
a
residence,
the
annoyance
of
aircraft
noise
remains
just one of the considerations that affect the market
value
of
a home
Exh.
229,101.
As will
be discussed in some detail
in another
section,
the
EcIS concluded that noise decreased property values.
The use of
the
regression analysis method estimated a mean 0.58 percent
decline per decibel increase.
The inverse condemnation method
indicated that reducing noise from 80
to 65 Ldn would
add
17
percent
to property value
(Vol.
II
at
93).
In addition to the loss of property value, noise impacted
persons complained of extra costs associated with responding
to
noise.
The Bensenville Home Society’s addition
increased in cost
by 15
to 20 percent because
of insulation, special windows, and
other sound deadening features.
The Society
“sees no
justification for paying this cost,
seeing that we have been here
since 1839
sic
at various places
in the record
the
founding date
of this facility is given as 1839 and 1894.
Since both predate
the airport,
this discrepancy does not undermine
the thrust of
the testimony.
,
long before
the airport was ever conceived of”
(R.
309).
Similar
feelings were expressed by a member
of
a
church which had
to be specially designed
to keep out noise
(R.
173).
Officials
at Maine Township High School South spent
$700,000 reducing noise impacts
(R.
463).
A Chicago resident
estimated that he spent about $100 per month on air conditioning
to keep out airport noise
(S.
44).
A Bensenville woman summed up
the feelings of many witnesses when she said:
I would appreciate this hearing taking
into full
consideration
the
fact
that
one
group
of
people
is
being asked
to pay a price
for the benefit of another
group
of people....The
point
is
we
are paying
their
freight
in terms of noise and inconvenience.
69.106

—43—
INDUSTRY CONCERNS
While citizens complained
about
their existing noise
problem,
industry representatives made a case for continual
service.
They almost universally based their testimony on the
worst case assumption that the noise regulation would require an
end to night
service and greatly reduce daytime flights.
Such
reductions would undoubtedly harm businesses dependent upon the
status quo.
As to the possible impact of regulation on business,
the Board will quote a representative sample of their comments.
Curtailment of daytime flights and the cessation of
nighttime flights would severely impact the air freight business
as indicated by a spokesman for
a Rockford
firm who also
represented the Aerospace Industries Association of America:
The
regulations
here
at
issue
pose
a
severe
threat
to
business.
The
nighttime
closing
of
Illinois airports, especially O’Hare,
arid the daytime
restrictions
mandated
by
Attorney
General
Scott’s
proposal
would
have
disastrous
consequences
throughout
the country.
Within the Midwest, much business that relies
to
any degree
on air transportation will not
be
able
to
compete due to the resultant inability immediately to
fill orders and ship them out.
Midwest
firms
dependent
on
suppliers
in
other
areas need 24—hour direct freight service
to maintain
manufacturing schedules.
In many cases,
these
firms
located
near
Chicago
because
of
O’Hare’s
excellent
air
freight
schedules.
All—cargo carriers generally
stop at O’Hare on both east and westbound flights....
The
proposal
would
also
have
a
significant
adverse
impact
on transcontinental
and
international
traffic
now
using
O’Hare
as
a
“gateway.”
Shipments
from
the
West
Coast
to
the
Midwest
will
have
to
depart
Los
Angeles
prior
to
5:00
p.m.
Pacific Time.
Shipments
to
be
interchanged
at O’Hare will have
to
leave Los Angeles before 3:00 p.m.
Shipments
into Los Angeles
through Chicago will
arrive
in the afternoon
instead
of
the present early
morning
deliveries.
Efficient
manufacturing
operations
rely
on
evening
departures
and
early
morning
deliveries
to
ensure
constant
production
schedules.
Those
suppliers
unable
to
route
around
Illinois
will
be
at
a
severe
competitive
disadvantage....
Most
of
the
involved
traffic
cannot
be
shifted
to
motor
carriage.
Air
transportation
meets
a
69-107

—44—
special need.
Companies shipping by air on
a regular
basis do
so for competitive reasons or because
of the
nature of
their product
ER.
4855—4857
There was also testimony by industry indicating that they
require reliable flight scheduling at all times
to remain
competitive, especially at O’Hare.
A Flying Tigers air freight
representative testified as follows:
Manufacturers,
wholesalers
and
retailers
all
depend
on
reliable,
scheduled
air
freight
services
for
good economic
reasons.
One
key concern
of
this
shipping
community
is
the
inability
to
predict
fluctuating
demand
in
volatile
marketplaces
around
the world.
Another
is the need
to stock and restock
key
components
inventory
at manufacturing plants
as
an
alternative
to
surface
transportation
modes.
A
third
factor,
...
is that the
relatively low cost
of
air
freight
compared
to
the
value
of
inventory,
is
more
than
compensated
by
having
a
product available
when and where
it
is needed....
Air freight in Chicago and throughout the State,
and
throughout
the
country,
has
become...a
competitive
tool
with
respect
to
other
domestic
and
overseas locations....
So
the
conclusion
to
us
is
apparent.
In
order
to
remain
competitive
with
both
U.S.
and
foreign
firms,
Illinois manufacturers and shippers must have
reliable
prime
time
scheduled
air
freight
services
available at O’Hare
and
other airports
in the State.
ER.
4715—17
A representative of John Deere and Company,
a manufacturer
of agricultural, industrial and construction equipment,
testified
concerning
the company’s emergency spare parts program for
machines
it manufactures.
He stated:
In
conclusion,
we
want
to
emphasize
that
time
delays
in
the
agricultural
and
the
industrial
and
construction
industries
can
be
extremely
critical.
That
is
why John Deere made
a
commitment
to
owners
and operators
of
our equipment
to make
repair
parts
for
an
inoperative
machine
available
at
the
appropriate
dealer
anywhere
in
the
U.S.
and
Canada
within
24
hours....Curtailment
or
cancellation
of
night
flights
at
O’Hare
will
have
a
substantial
negative impact on this program
ER.
4836
Likewise
a representative of Sperry Univac presented the
following testimony:
69-108

—45—
Sperry
Univac
is
engaged
in
the
development,
manufacturing,
and
sale
of
computers
and
component
parts
thereof.
Our
Worldwide
Parts
Distribution
Center
is
located
in
Elk
Grove
Village,
adjacent
to
O’Hare
Airport
and
is
located
there
specifically
to
take
advantage of the large number of flights available at
all hours.
There
is
no manufacturing
at
Sperry Univac
Elk
Grove.
It
is
a
distribution
center
for
computer
parts,
with
the
responsibility
to
service
any
point
in the world.
Last year,
Sperry Univac Elk Grove shipped $232
million
worth
of
parts
by
air.
This
consisted
of
38,164 shipments weighing 465,000 pounds domestically
and
5,700
shipments
weighing
868,000
pounds
internationally.
Some
87
percent
of
those domestic
shipments
and
two
percent
of
the
international
shipments
moved
on
flights
between
10:00
p.m.
and
7:00 a.m.
The
task
of
the
Sperry
Univac
Worldwide
Distribution
Center
is
to
fulfill
our
commitment
to
our customers,
that any replacement parts needed will
be
supplied within
24
hours domestically,
and within
48
hours
internationally.
If we fail
to do this,
we
suffer
economic penalties
as stipulated by contract,
and
further,
collect
no
revenue
if
a machine
is
not
functioning.
In
order
to
accomplish
these
tasks,
Sperry
Univac elected
to relocate its Worldwide Distribution
Center
from
Ilion,
New York,
to
Elk
Grove,
Illinois
in
mid—1971.
The
choice
was
simple.
Chicago’s
O’Hare Airport provides
a centralized location with
a
tremendous
lift capability.
Reduction
in the amount
of
lift
at O’Hare would
seriously affect our ability
to perform
to
our service standards and
force
us
to
relocate
the
distribution
center
to
an
area
more
sensitive
to the needs
of the business community
R.
4702—04.
In addition
to normal air
freight,
critical medical
equipment
is shipped
from O’Hare as indicated by the Manager
of
Regulatory Affairs for Abbott Labs:
The
Diagnostics
Division
is
a
shipper
of
shortlife, perishable medical diagnostic test kits
to
hospitals,
clinics
and
medical
laboratories
throughout
the United States and the entire world.
69-109

—46—
Abbott maintains
a central distribution base
in North
Chicago
from
which
many
of
these
lifesaving
diagnostics are shipped.
The kits are used
to detect
serum hepatitis,
thyroid malfunctions, cardiovascular
problems
and
rubella.
The
vast
majority
of
these
kits
contain
radioactive
material.
A
great
number
must
be
shipped
with
dry
ice
to
preserve
their
integrity and
to prevent them from deteriorating.
Often,
customers call
for
immediate shipment
of
the
product by
air
to
alleviate
a
health
emergency.
situation.
In
many
instances
the
first
available
commercial
flight
leaves
O’Hare Airport
in
the
late
p.m.
Without
these
flights,
our products
would
not
be shipped until morning and could incur
a full day’s
delay
in delivery because trucking delivery schedules
at destination airports require shipment availability
from
the
airlines
at
the earliest possible
time
in
the morning.
The
majority
of
the
export
flights
best
suited
to A.D.D.’s needs departs between 3:30 a.m.
and 6:20
a
m
.
.
For
example,
orders
for
products
shipped
daily
to
southern
California
are
flown
via United
Flight
117
departing
O’Hare
at
9;30
p.m.
and arriving
Los
Angeles
11:35 p.m.
These shipments are recovered by
1:00
a.m.
and
delivered
throughout
southern
California the next day.
Northern
California
orders
depart
on
Flying
Tigers Flight 245
at 4:30 a.m.
for San Francisco and
are
on
their
way
to
customers
by
8:00
a.m.
This
pattern
is
repeated
to customers
all over the United
States....
In
order
to
service
our
customers’
emergency
medical
needs,
around-the—clock
departures
are
an
absolute necessity.
A
logical
alternative
to
this
system would,
of
course,
be
to
stock
these
products
at
multiple
locations
but
this
would
mean
stocking
highly
perishable
nuclear
materials
at
a
number
of points.
Because
of
a
relatively
short
shelf
life
on
a
majority
of
these
products,
usually
not
exceeding
forty—five
days,
the
need
for
disposing
of
expired
material
would
dramatically
increase.
This
would
only
serve
to
add
to
an
already
serious
national
problem of nuclear waste disposal.
It
is
our
opinion
that
elimination
or
curtailment
of
air
cargo services during what is now
69-110

—47—
known as
“prime time,”
i.e.,
late p.m. and early
a.m.
would
be
disastrous
to
what
has
thus
far
been
a
highly
successful
system
for
distributing
high
priority medical
diagnostics
to
the worldwide health
community.
ER.
5300—07.
The Corporate Traffic Manager
of Travenol Laboratories of
Morton Grove said:
Travenol
Laboratories,
Inc.
is
a
worldwide
manufacturer
and
distributor
of
intravenous
solutions,
blood
collection
equipment,
hospital
disposable
kits
and
artificial
organs,
including
kidney dialysis machines
and
supplies, which
employs
more
than
8,000
men
and
women
in
Northern
Illinois....
During
1979,
we
made
16,340
air
freight
shipments
from
Morton
Grove
ard
the
Northbrook
facility.
These
shipments
totaling
over
976,000
~5oundswere
all
classified
as
“medical
emergencies”
by our accounts which are basically hospitals,
kidney
dialysis
clinics
or,
blood
reception
centers.
The
shipments
which can consist
of any
of our over
1,200
life
support
products,
are
destined
to
any
part
of
this country
from the
largest city
to
the smallest
unincorporated area.
We accept orders
at our Customer Service Center
in
our
Deerfield,
Illionois
Corporate
Headquarters
until
4:30
p.m.
daily.
“Medical
Emergency”
orders
are
transmitted
electronically
to
our
Morton
Grove
Distribution
Center
after
4:30
p.m.
daily.
These
orders
are selected
by
our
2nd
shift
personnel
that
evening
and
are
picked
up
that
night
by
our
air
freight
forwarder
for delivery
and movement
on
that
night’s
freighters.
As many as
80 shipments per day are
received and
shipped
in the manner outlined above.
O’Hare Airport
with
its
great
capacity for destinations serviced
by
air
freight,
is
the
key
element
in
our
medical
emergency
delivery
capacity.
Our
customers
have
learned
to
rely
on
us
for
life support
systems.
We
have
learned
to
count
on
the
air
freight
service
available from O’Hare.
Should
O’Hare
terminate
service
between
10:00
p.m.
and
7:00
a.m.,
our
customers
in
need
could
not
get
next
day
delivery
since
over
85 percent
of
our
order
for
this
type service are received late
in the
afternoon....
Any closing
of O’Hare would have serious effects
69-111

—48—
on our customers since certain product lines, because
of
their
very
nature,
are
only
stocked
at
one
location
——
Morton Grove.
Thus,
emergency service
to
our
customers
would
be
two
days
——
not
one
day
as
they
now experience
——
unless
we were
successful
in
delivering some shipments
to Milwaukee about 75 miles
away
R.
5277—82, emphasis
in original.
Emery Air Charter operates an airborne intensive—care unit
from Northwest Community Hospital
in Chicago.
Their
representative said:
We
operate
a
fleet
of
jet airplanes
throughout
the
western hemisphere
on
a medical
transfer
basis;
besides
which
we
operate
the
same
airplanes
in
a
corporate
transport
configuration
in
the
same
area.
.
We
carry
heart
monitors.
We
carry
automatic
suction devices.
We carry respirators
——
In layman’s
terms,
it does the same thing as the
iron lung,
or
it
breathes for the patient.
We carry
any
other
traction
device
that may
be
required
for
spinal
injuries
or
for
necks
and
backs
——
that type of
thing....
We
use
an
airborne’
monitoring
system
very
similar
to
what
you
see
on
your
television
on
Saturday
night
on
EMERGENCY,
where
the guy plugs
the
phone into the monitor and sends
the vital signs
into
the hospital.
It
sounds
funny
to
say
it’s
like
the
thing
on
television,
but it’s very serious.
We
have
transferred
the
last
three
heart—
transplant
patients
done
in
this
country
to
the
hospital monitoring the heart at all times....
We service virtually every international carrier
that
flies
into
the United
States.
We
service
90
percent of the domestic carriers
in the United States
——
No,
it’s not at all local
ER.
1337—1341.
At the time of the hearing, Emery was expanding
to Greater
Rockford Airport where they expect
to be able
to operate at all
hours.
Currently,
25 percent of their operations are
at night.
They average four movements per day from Rockford
ER.
1341—48
A representative of Emery Air Freight Corporation
testified
as
to the damaging
ripple effect that can result with schedule
changes:
69-112

—49—
All
arrivals
and
departures
are
arriving
from
and departing
to somewhere else.
Therefore,
a curfew
at
a
particular
airport
will
impose
“effective”
curfews
at
other
airports,
a
situation
which
is
compounded as more airports are curfewed.
Further
evidence
of
the disruptive capabilities
of curfews and as
a result of the “effective” curfews
presented
above,
is
the
topic
of
“scheduling
windows.”
Given
effective
transit
times
and ground
time
constraints,
as
well
as
the
other
scheduling
factors
mentioned
earlier,
various
curfew
scenarios
will
create
time
slots
only within which flights can
operate
and
observe
the
various
operating
and
competitive constraints.
ER. 4620—271.
A representative of
R.R. Donnelly,
the largest commercial
printer
in the country, which is Chicago—based, testified
as
to
the
importance of around
the clock service
to his company:
Attached
as
Exhibit
1
to
my
testimony
is
a
schedule
of
air
shipments
for
the November
19,
1979
issue
of The New Yorker.
This schedule
is
a singular
indication
of
the
weekly
shipping
volume
of
the
magazine which
is produced
in Chicago.
The schedule
includes
91 air
shipments
from O’Hare, most
of which
are destined for nationwide newsstand distribution.
To
meet
the
customer’s
schedule,
Donnelley
begins producing complete copies
of The New Yorker
at
1:00
a.m.
Tuesday.
And
as
soon
as
sufficient
quantities are produced,
R.R.
Donnelley’s own
trucks
begin
hauling
air
containers
of magazines
to O’Hare
Airport
for
precision
dispatch
to New
York
for
the
prime market distribution.
This
first
truck
must
leave
the
Donnelley
facility
by
5:30
a.m.
to make
the
dispatch schedule
for
the early container flight at 7:05 a.m.
At least
four
other
truck
dispatches
are made
throughout
the
course
of the day
to bring
a timely flow of shipments
to O’Hare for distribution to the proper airline.
To
further
amplify
the
critical
service
standards
of
our
customer,
the New
Yorker
requires
that:
1)
Shipments
of
200
copies
or
more
must
be
delivered
to
the
individual
wholesaler
by
6:00 p.m.
Tuesday,
2)
Shipments
of
100—199
copies
must
be
delivered
to each wholesaler by
6:00 p.m. Wednesday,
and
3)
Shipments
of
up
to
99
copies
may
be
mailed
second
class,
but
are
to
be
hauled
to
seventeen
postal entry points with subscriber mail....Regulated
common
carriers
do
not
openly
solicit
this
type
of
freight.
O’Hare
provides
the most direct flights
to
69.113

—50—
the
greatest
number
of
points,
and
provides
the
necessary backup flights
to meet our tight production
and
delivery
schedule
as
indicated
by
the
above—
mentioned exhibit.
.
The New Yorker
is not
the only weekly we have at
Chicago.
Others
include
TIME,
People,
and
Sports
Illustrated,
all
of which depend on quick delivery of
dated
material.
Donnelley prints
these weeklies
at
Chicago
and
at
other
locations
at
premium
printing
costs for short
runs....
The
above—mentioned work
is
a
small
percentage
of
our
volume
funneled
through
O’Hare.
Newspaper
inserts,
or
tabloids as
they are commonly known, have
insertion
date
deadlines.
We
print
millions
of
pounds and ship to hundreds of newspapers
for catalog
customers,
such
as
Sears,
Penney’s,
K—Mart,
Ward’s
and others....
R.R.
Donnelley’s
Chicago Division transports
by
air
over
300
packages
of
financial
printing
per
month.
Financial
printing
is
comprised
of
prospectuses,
securities,
annual
reports,
et
cetera.
The printing cycle
of this product requires
attorneys and
issuers
to remain on site on
a 24—hour
basis
in order
to verify
final proofs prior
to final
printing....
If
we
were
unable
to
provide overnight service
through
our
three—shift
operation
and
all—night
air
transportation,
there
is
no
doubt
that our customers
would print this work elsewhere....
Our
Dwight
Manufacturing
Division
prints
a
number
of
restricted
credit
card lists
or
“hot card”
lists
weekly
in
quantities
of
millions.
They
are
distributed
as
first
class
mail,
and
on
a
weekly
basis
120,000
pounds
of
mail
leaves
O’Hare
during
nighttime
flights.
If
air
service
is
reduced,
we
anticipate
that
Donnelley’s
credit
card
customers
may,
as with other
customers previously noted,
begin
to look at alternate printers with better air service
capabilities.
These
customers
simply
cannot
wait
even one extra day for distribution of their product;
if
they
did,
the
usefulness
of
the
weekly
listing
would
be
minimal
and delay could,
in fact,
result
in
cards
already
known
to
be
stolen
or
lost
being
accepted by local merchants.
Our
Elgin
Manufacturing
facility
produces
computerized
typesetting
on
Yellow
Page
telephone
director advertising.
Our sales representatives
sell
this preliminary work on the basis
of overnight turn—
69-114

—51—
around
on
page
proofs
to
show
their
advertisers.
There
are
approximately
208
of
these
shipments
annually, and they are handled exclusively
by Federal
Express....One
day
lost
on
distribution
of
proofs
could
negatively
affect
the
major
portion
of
seventeen
percent
of
our
directory
work
ER.
4884—
4892
Representatives of the banking industry testified that any
resultant reduction in service levels at Illinois airports, and
particularly at O’Hare International Airport, will cause
irreparable damage
to the banking system of Chicago.
A quotation
from the American Banker
(March
31,
1978)
aptly describes
the
problem.
...checks,
unlike
people,
do
not
prefer
to
travel
in business hours.
To the contrary,
they are
not
cleared,
processed
and
ready
to
head
for
the
airport
until
the
business
day
is
over.
And
this
means
that,
with
the
cutting
back
of
airline
schedules,
the
checks
are
ready
to
travel
just when
the
airlines
are
closing
down
for
the
night
ER.
4670
The United States Postal Service cites four effects
of
service curtailment at O’Hare:
The
receipt
and dispat~chof mail
in excessively
large
volumes
on
arriving
and
departing
morning
flights;
large
mail
volumes
affecting
sequenced
processing
and
the
choking
of
the
distribution
processing
system;
ojutgoing
mail
at
origin
points
backing up until transportation is available;
and
a
scarcity
or
unavailability
or
storage
space
for
processed
mail
awaiting
transportation.
Public
Comment
#20,
1—3—78
Concerning
the impact an airport noise regulation could have
on
the
regional economy,
the Chicago Association
of Commerce and
Industry witness said:
It
is
our view that
any
cutback
or substantial
alteration
in
the
level
of
that
service
could
profoundly
depress
local
economic
activity.
Since
O’Hare
field
opened
jet
transportation
in
1959,
it
has
been
the
greatest
economic
generator
in
the
history
of
Chicago,
has
played
the
greatest
contribution
to
our economic development
of
anything
that has happened....
A major
opportunity
for Chicago
is
to
become
a
great
global
city,
that
is,
a
crossroads,
a
hub
of
national
and
international commerce
——
a place
from
which
men
and
women
in
business
can efficiently
and
69-115

—52—
conveniently cover
their major markets.
Efforts are
being
directed
even
now
to
improvement
of
our
international
terminal
facilities
at
O’Hare.
We
should
be
looking
toward
expansion
and
not
curtailment.
To
be
global,
the
city must set
its
course
now
to build
on
its strengths and attract multi—national
corporations....
For Chicago,
being
a global
city will mean more
business,
more
jobs
and
a
better
quality
of
life.
Proximity
to
major
markets
and
outstanding
air
transportation service
are essential
ingredients
to
becoming
a global center.
Chicago now has
leadership
in
the
world’s
air
transportation
system,
and
this
gives us
an edge on other major competing cities.
Disruption
of
air
transportation
services
resulting
from
implementing
the
noise
regulations
proposed
by
the Attorney General
would
be
a
serious
blow
to
Chicago’s
stature
as
aviation
crossroads
of
the nation and international gateway to North America
R.
4491—97
The president of the Chicago Convention and Tourism Bureau
testified as follows:
Right
now,
our
efforts
and
those
of
our
allied
industries
in
Chicago
are
attracting
nearly
eight
million
visitors
each
year
to
the
City.
Nearly
5.5
million come
to Chicago for pleasure and 2.5 million
come to attend
a convention, trade show,
or corporate
meeting.
Together,
Chicago’s visitors
spend
$1.4 billion
each year while they are
in the City.
Using
a modest
dollar
turnover
of
four
for every dollar
spent,
this
means that the total
impact of the travel
industry in
Chicago
is more than $5.6 billion each year.
To give
you
another
comparison,
the
$1.4
billion
spent
by
visitors
to Chicago each year
is equal
to the
entire
budget of the City of Chicago....
But
I
can’t
emphasize strongly
enough
that
the
health
of
this
industry,
an
industry
that
employs
nearly 150,000 people
in Chicago,
would
be seriously
affected
by
any
curtailment
of
service
at
O’Hare
Airport.
For
example,
last
year
during
the
31
days
in
June
and
July
that
the
DC—lO’s
were
grounded,
our
visitor
index
showed
a
6
percent drop
in
the number
of pleasure visitors who came to Chicago.
Since the
69-116

—53—
grounding occurred
during
our
prime
tourist
season,
the
economic
loss
was
substantial,
more
than
$13.6
million.
In January,
when O’Hare
Airport
was closed
for
part
of
six
days
during
the
National Manufacturers
Housewares Association Trade
Show,
attendance
at
the
show
dropped
20,000
when
compared
to previous years
and the show that immediately followed....
For example,
in the convention industry, Chicago
currently
attracts
more
than
1,100
conventions
or
trade
shows
each
year
and
an
additional
16,000
corporate meetings are held hear annually.
They come
here
because
of
the
City’s
outstanding
meeting
facilities,
its
large
number
of
top
quality
hotel
rooms,
and
its
accessibility
through
O’Hare
Airport.
Some
78
percent
of
the meeting
attendees
come
to Chicago by plane....
With O’Hare Airport operating
in an unrestricted
manner,
we
are
able
to
sell Chicago as
a
city where
anyone
in
the continental United States
is
less than
four
hours
by
jet airplane
from Chicago.
With more
flights
than any other
airport
in
the world,
Chicago
is
easily
the
world’s
most
accessible
city.
This
advantage
is
often
a
key
factor
in
selling
a
convention’s
site
selection
committee
on
coming
to
Chicago.
If
we
were
to
lose
this
advantage
because
of
restrictions on the number of flights into and out
of
O’Hare,
we
would
suffer
in
our
convention
industry....
Clearly what
is
needed
to help Chicago’s travel
industry
grow
is
expansion
of
O’Hare
Airport,
not
restriction.
Because of the deplorable international
terminal,
Chicago
has
barely
tapped
the
lucrative
European travel market
R.
5823—5827).
DEVELOPMENT PATTERNS
The conflict between airport users and residents around the
airport has escalated
to unprecedented proportions.
Some persons
living
in noise impacted homes moved there with full knowledge
that an airport was
located nearby.
Others are victims of a
variety of circumstances that were largely beyond their control
such as changes
in aircraft types,
airport expansions, new
runways and operational changes.
Mr. Edward G.
Studholme,
who has
a Masters degree
in urban
and regional planning and
is an aviation noise consultant,
pointed out the two major reasons the airport noise problem has
69-117

—54—
become so severe:
On
the
one
hand,
we
have
the airports
which
in
1959
or
1960
began
requiring
a
tremendous
amount
of
acoustical
space
for
their operations
because
of
the
introduction
of
jet
aircraft.
This
was
further
enhanced
or
made more
severe by
the
fact that
there
were great
increases
in
the
number
of
operations at
those
facilities
and
because
of
the
capacity
of
strength
and proliferation
in
flight
tracks
and
in
some
cases
in
the
number
of
runways
and
the
directions
of them.
So,
this noise contour which we
keep
talking
about
grew
by
order
of
magnitude
sometimes five hundred
or
a
thousandfold
in
an
area
just due to a change
in technology.
On
the
other
hand,
we
have
had
a
tremendous
amount
of encroachment
of
incompatible land use upon
airports
that has
been attested
to
here previously,
the
proprietors
very
rarely
have
any
control
over
this encroachment
ER.
2347—48.
Move to the Airports
Ms. Jill Tiedt,
a senior associate with Landrum & Brown who
has a Masters degree
in urban planning, studied development
patterns around O’Hare and Midway airports.
She used aerial
photographs dating back
to the early
‘60’s and some ‘50’s,
interviews with local officials and the 1971 Metropolitan
Aircraft Noise Abatement Policy Study (MANAPS, Exhibit 223 B—
1).
According
to the MANAPS
report, O’Hare Airport,
known both
as Old Orchard Airport and the Douglas Aircraft Assembly Plant
Field, was developed
in 1943 as
a wartime project.
The original
airfield consisted of four runways.
Over the years,
five master
plans have been developed for O’Hare Airport.
In addition,
numerous minor modifications were made.
These included runway
extensions
and widening.
Two additional runways were added, one
in 1967 and the other
in
1971.
Although substantial
development
existed
in the O’Hare vicinity prior
to
1950, much of the area
was developed after
the airport became a major facility.
She
described incompatible development in terms of
“infill” or
building new homes
in established subdivisions,
and “new
development.”
As examples of growth
in noise impacted
communities,
she stated that Bensenville’s population grew 144
percent between 1950 and 1960 and another
40 percent
by 1970.
Wood Dale grew 65 percent between 1950 and 1960 and
an additional
188 percent by 1970.
The neighborhoods surrounding Midway were
well established prior to the introduction of jet aircraft.
In
four of
the five Chicago community areas surrounding Midway less
than 15 percent
of the housing was constructed after
1960.
She
described the Midway problem as
“a result of changing aircraft
technology rather than poor planning”
and pointed out that “noise
from propeller driven aircraft used
in the commercial fleet prior
to 1958 was not generally viewed as
a serious public policy
69-118

—55—
issue”
(R.
6217—6228).
In examining housing unit counts
for sections of Addison,
Elk Grove,
Maine, Bloomingdale and Leyden townships, Tiedt found
considerable
new construction since
1970:
In the period from April
1970 to April 1978,
517
single
family
units
and
784
multiple
family
units
were
constructed
in
areas
which
were
already
noise
impacted
and
which
in
1974
were
exposed
to
noise
levels
of
75
Ldn
or
greater.
Similar
trends
exist
for areas contained within the
80 Ldn contour and the
85 Ldn contour.
Indeed,
during
this
same
period
of
time,
31
single family units and
70 multiple family units were
constructed
on
land
which
in
1974
was
exposed
to
noise levels of 85 Ldn or greater
ER. 6245
Several
witnesses
commented
on
the
fact that airports
seem
to attract development
that will
be impacted by noise.
According
to law school faculty member,
Sheldon Plager:
One
of
the
remarkable
things
about
the
lemming
behavior of the American citizen
is that the
idea has
been
to put
the
airport
out
away
from where
people
live,
and
that
has often been
the case,
and
as
soon
as
that happens,
everybody moves
to the
airport.
As
soon
as
they get
located,
they
start
bitching
about
the noise.
Now, one could
say this sort of
a hardnosed way
——
“Well, you deserve what you get,” but that has not
been
the way
we
have dealt with
these problems,
and
probably
ought
not
to
be
the
way.
So
we
end
up
frequently
with
a
situation
in
which
the
airport
becomes
impacted
in
part
by
its
own
lack
of control
over
its
environs,
and
in part by
the
fact that
the
market
operates
in
such
a
way
as
to develop
around
the
airport,
because
a lot
of people
seem
to
like
to
live there
R.45.
Studholme pointed out some of the attractive features that
make
it difficult for local authorities
to prohibit residential
development near airports:
The major
factor
would
be
the attraction
——
the
actual
physical
attraction
——
of
incompatible
development
by airports.
People
don’t
just want
to
live around airports, they want to live there because
it’s an ideal location to develop property.
Airports
are sited
in areas where the land
is flat, where
it’s
drained, where there
is
a minimum amount of
a problem
with
the
vegetation,
and
then
subsequently
the area
69.119

—56—
is provided
with
an
adequate water, sewer,
drainage,
very efficient ground transportation access.
These are exactly
the criteria
that
a developer
would
look
for
in
trying
to
locate
new
residential
land use
R.
2349)
Dr. William J. Galloway,
a physicist and a general aviation
pilot, who holds
a Ph.D.
in physics and
a Masters degree
in
applied physics, suggested that people moving into a noise
impacted area often are not aware
of the magnitude of the problem
until they have lived
in the area
a while:
I think
the fact that the people who move into a
lot
of
these
areas
are
not
aware
of
what they
are
doing.
I
think they are sometimes uninformed of what
the noise environment
is
ER.
5497
I
think,
really,
I
think
the
whole
thing was
addressed
to
why
do
people
move
into
homes
near
airports.
I
say
I
think
the
answer
is
first,
they
want
to move there and
if
the question
is can they or
can
they
not
abide
with
the
noise
is
really
a
question
of
they
have
moved
in,
not
necessarily
having
an
understanding
of
the
magnitude
of
that
noise.
Once
they
are
there,
they are
in
a position
to
determine whether
or
not
the
other
attributes
of
that living environment
are ones they are willing to
live with or
not....ER.
5707.
An Elk Grove Village resident made
this point
at
a
supplemental hearing when asked
if planes were present when he
looked
at the house:
There
probably were.
But
it was something that
you weren’t really aware of and never considered.
In
other
words,
it
didn’t
enter
your
mind.
I
mean,
occasionally
——
we
lived
further down
in
the
city,
occasionally
we
would
hear
an
airplane,
you
know.
But
it
wouldn’t
really
bother
us.
I
mean,
an
occasional
airplane
every
couple
of
hours
wouldn’t
really
bother
me.
But
when
one
is
every
three
minutes,
you
know,
flying
right
over
your
house,
it
gets
to be very annoying
(S. 207—8).
Airport Changes Impact Residents
Although people have moved closer
to airports,
in many
instances populations already present are impacted by changes in
airport operations
or airport expansion.
One
of
the most
dramatic examples
of residents being impacted by
a new airport
was contained
in the testimony of
a Bensenville
resident:
69-120

—57—
I
might
add
that
the
Bensenville
Home
Society
has
been
in
existence
in
that
location
since
1894,
long
before
the
airport
O’Hare
was
even
dreamed
about.
R.
5842
In earlier testimony the Director of Engineering for
the
Society stated that the Society had recently added a 250 bed
nursing home and was proceeding with a 149 unit apartment
building
for the elderly on the same site with HUD funds
(R.
307).
When asked
if the Society would have opposed noise zoning
regulations on the use of
its property he
responded:
I would
think
so.
We have been here since
1839
sic
,
I think we have some rights.
We were actually
asked
by the Village
of Bensenville
in 1839
sic
to
establish
our
home
for
the aged
and orphans at
that
time.
And we see no reason why we should
be asked
to
give
in
because
some
industry
wants
to
make
more
noise
over our head
ER.
313.
Changed airport operations are also
a problem and are akin
to the situation where the people are there before the airport.
As one Park Ridge resident testified:
However,
at
the
time
we
moved
in
the
landing
procedure
at
O’Hare
Airport
was
different,
and
I
lived
in
an
area
relatively
close
to
that
for
a
period
of
eight
years.
So
I
thought
that
I
had
a
fair
idea of the type of landing procedure used.
But
obviously
I hadn’t.
ER.
124—5.
A resident from Sugar Grove Township testified:
Up
until
last
year
the
Aurora
Airport
was
strictly
for small planes.
Most of us moved
into the
area,
never thinking
the airport would be
a threat.
Then Aurora waived
its restrictions
and allowed
a
Gulf
Stream
II
jet...to
be
based
at
its
airport...the
FAA
cited
the
Aurora
Airport
as
a
satellite airport
for O’Hare
and wishes
to make our
airport
appealing
to
corporate
business
traffic.
This
is
very threatening
to the
residents.
R.
4167—
8
A Des Plaines resident testified that:
when
we
came into this territory,
the City of
Chicago
did
not
own
the
property
north
of
Higgins
Road.
They bought the property between Higgins
Road
and Touhy
and
then rerouted Higgins Road up over the
overpass at the Kennedy Expressway and then on out so
that
the
property
——
we
now
live
a
Hell
of
a
lot
closer
to
the airport
than
we
did.
That’s
because
69-121

—58—
they
bought
it
and
maybe
next
week
they
will
buy
another piece.
R.
4350.
Midway Airport provides
a good example of the impact of
a
change
in airport operations.
One Chicago resident commented on
past and current operations:
I
have
lived
there
during
the
time
when
the
runways
were
dirt,
cinder,
and
so
forth.
I
saw
Lindbergh bring
mail
in there.
I saw this when this
was
the
busiest
airport
in
the
world,
and
no
one.
complained.
Planes
went
up and down.
But
they are
not like they are today, with the jets.
Now they got
new jets that come
in there, whish over,
and they are
not
bad
at
all.
But
these
old
ones
are
absolutely
unbelievable.
We
have
people
that
are
sleeping
within 500 feet of the take—off of
these planes....In
fact,
one
half
mile
from
that
take—off
point
the
ground actually shakes underneath your feet
S.
77.
One woman said that she was seldom bothered by noise until
the Air National Guard
at Springfield obtained
F4 Phantom jets
(R.
1518), which were described as noisier than the prior models
by an airport official
(R. 1502).
A woman from East Alton
testified that jet fighters and commercial jets had only recently
begun flying over her home making touch and go landings.
Her
mother
had lived in the same subdivision for
14 years.
She
responded as follows
to the question of whether she was aware
that the house was under
the airport approach pattern when she
bought
it.
It
was
under
the
approach
pattern
for
small
aircraft.
We
knew
that
there
was
never
any
jets
coming
in, Ozark had not started coming
in,
there was
never
any
jets.
Okay,
as
far
as that was concerned,
we knew about the small.
There had
been
a thing
going
on where they were
trying
to
get
them,
but
the
airport
was
much
too
small
to
have
larger
planes.
Air
Illinois
come
in
there
for
a
while.
They
did
not
come
over
our
subdivision,
they
were
using
a
different
pattern
where
they
took
off
over
empty
fields
and
it wasn’t
effecting
anyone,
there
was
no complaints
from
that
because
they
were
not
loud
noises
and
they
didn’t
come
in
to
where
they were
about
to
touch
the
tree
tops
either.
They were landing
and
taking
off
from
over
the
farm
area,
not
over
residential
area.
B.
2262—63
Others purchased land when runways were under construction
or repair
for months at
a time.
A Des Plaines resident bought
his home “while
O’Hare Airport runway 22R was under
construction and not
in use.
The neighborhood,
then, was not
69-122

—59—
subjected
to the continous bombardment of noise and pollution
that started to exist again
after the runway was reopened”
(S.
190).
A Bensenville woman had similar testimony:
A lot of people all say to me,
“Why did you move
to Bensenville.
Didn’t you know
it was close
to the
airport.”
When
my
husband
and
I
bought
a
lot
two
years
ago
this
month,...it
was
summer
of
1975 when
they were resurfacing
the runways, we built for about
four
months.
We
didn’t
see
a
jet
in
any direction.
We saw
nothing.
We were
at
the
job
site every
day
for
14 hours
and never saw a jet.
We
moved
in,
it
will
be
two
years
next
week.
The
jets
did
not
stop
flying
the
first
session
for
about
ten days....
That
first two weeks we lived
there
I called the
FAA and said “Hey, what
is going on.
Where did these
jets
come
from?”
And
a very nice man,
Mr.
Callahan
said
——
and he was very
kind,
he said,
“Well,
didn’t
you
know
that
there
were
any
jets
there?”
I
said,
“Sir,
no,
I
got
a
permit
to
build
and
I
built my
house,
nobody
said
anything
about
this
side
of
town.”
I
am
at
the
west
end
and he
found
my
house
on
his map and he said that the jets
fly 400
feet over
my house.
He told me that quote
I was one mile from
the tip
of the
runway.
He said that was a very well
used
runway whenever
there
was
an easterly wind
B.
399—410
The problem of unwitting buyers can be compounded by agents
who sometimes take advantage of prospective buyers because of the
lack of disclosure requirements, according to a study
commissioned by the Department of Energy and Natural Resources:
The
effects
of
aircraft
noise
on
homes
near
airports
can
be
viewed
as
latent
property
defects.
Because the noise levels vary throughout any day, and
because
the
effects
can
be
cumulative,
resulting in
injury
or
annoyance
only
after
a
period
of
time,
a
prospective
buyer
or
tenant may
not become aware
of
the
noise
problem
until
after
the
land
transaction
has
been
finalized.
Sellers,
lessors,
and
their
agents
Sometimes
engage
in
practices
intended
to
disguise noise
conditions.
For example,
real estate
agents
are
known
to
have shown houses
to prospective
purchasers
only
during
non—peak
air
traffic periods
Exh.
239,
116—117
Tiedt complained that local
realtors and developers are
under
no obligation
to warn potential buyers of noise impacts
(R.
69-123

—60—
6279).
This fact was generally confirmed by local officials
(B.
320 and 453).
Schools and Hospitals
The construction dates
of schools and hospitals also show
that some predated the noise problem while others were built
in
impacted areas.
For example,
the Superintendent of Schools
in
Bensenville District Number
2 and 100 testified that:
What
about
the
operation
in
the
classroom;
in
the fall and spring we can’t open windows and we have
old buildings,
Fenton High
School was built
in
1954,
I
think
that
was
about
the
time
O’Hare
started
to
work
out;
Blackhawk
Junior
High
School
was built
in
1956,
that was
after
O’Hare.
We
have
no excuse
for
Blackhawk.
Greenstreet 1915,
that was before O’Hare
was
thought
of,
Tioga
1931,
Chippewa 1926,
Mohawk
in
the flight path 1955, Johnson 1958.
ER.
287.
The Superintendent of Leyden School District 212 testified:
I
came
to
the Leyden community
in
1958,
and
at
that time why Midway was
the main airport.
And all
of East Leyden,
all
of our students at that time were
in
the
East
Leyden
building
and
we
had
all
of
our
buildings
with
open
windows
and
no
noise
problems....West
Leyden
then
became
in
use
in
1960.
It
was
a
new
building
and
everything,
and
at
that
time we
had no air conditioning and
a
lot of windows
because
there
still
was
practically
no
traffic
at
O’Hare compared to Midway.
But,
it soon changed.
In
1960, O’Hare started experiencing growth.
B.
334—6
The Superintendent further testified that noise—proofed
additions and reconstructions were completed at West and East
Leyden, incorporating the use of windowless walls and air
conditioning.
The Superintendent of School District
81
in Schiller Park
testified as
to the age of
the school buildings
in his district:
Well,
the
school
district
has
been
there
for
many years.
Our oldest erected building
is 1924, our
last
building
was
in
1967.
Of
course,
it
is
a
mystery
why
that
building
was
allowed
to
be
built
less
than
a
half
mile,
less
than
five—eighths
of
a
mile,
three blocks,
from one of the runways at O’Hare
Airport,
George
Washington
Elementary
School.
Why
it was even
built
is
a mystery.
Why homes
and
school were
built
in that area
is
something that
we are puzzled about to this day.
But the fact
69-124

—61—
remains
that
it was built
and there are people
there
S.
70..
Of the three schools that have been soundproofed with
federal funds, Washington was built approximately
in 1964
(S.
269), Orchard was built
in 1947
(R.
976,
1030),
and Mohawk
in
1955
(R.
287).
Exhibit 223 B—l tabulates
the names of eleven hospitals
surrounding O’Hare whose exteriors are subjected
to at least 65
Ldn (Table 12
at 51—2).
Also tabulated are data for the year
built, when additions were added,
construction type, number
of
beds, whether federal grant funds used, how often affected by the
noise, and mitigatory steps.
The three hospitals most affected
by airport noise are Lutheran General
in Park Ridge, Resurrection
in Chicago and Memorial
in Elmhurst, built respectively in
1960,
1953 and 1926.
These hospitals have had subsequent additions.
Land
Use
and Zoning Concerns
Airport authorities have long recognized
the problems caused
by noise and have urged zoning boards and other authorities
to
limit development
in noise corridors.
Their efforts have met
with
little success.
The Springfield Airport Authority objected
to twelve zoning cases and lost them all.
The Springfield
Airport manager testified that:
no,
we
have
no
control
whatsoever
over
any
lands
that we
do
not
own.
There are
no provisions
either
by
zoning
——
We
objected
to
12
different
zoning
cases
involving
property
adjacent
to
the
airport,
and
we
lost
all
12,
and we
have
none.
ER.
1484.
The Bloomington—Normal Airport Authority objected but lost
in
a zoning case where
a housing development sought rezoning
of
an agricultural parcel
to medium density residential.
The
airport manager testified that:
Lin
the
past
it
was
the
Airport
Authority’s
intent
to
lengthen
this runway when
the
need
arose.
In
1974,
however,
a housing development
located just
southwest and
in line with the runway was approved by
the Bloomington City Council.
The Airport Authority
and
I
objected
to
the
zoning
changes
from
Agricultural
to Medium Density Residential.
In fact,
we
fought
with
every
possible
means,
but
to
no
avail.
The
end
result
was
that
we could
no
longer
plan
to
lengthen
the
runway
to
accommodate
larger,
noisier
aircraft.
We
had
to
make
other
plans.
ER.
2000
69.125

—62—
However,
the development of
a
48 unit apartment complex was
successfully halted by the Mount Vernon Airport Authority when
the authority introduced evidence at the zoning hearing.
A
consulting engineer for the authority testified that:
A
housing
developer
planned
to
build
a
48
apartment
complex
financed
by BUD,
within
1250 foot
of the primary runway at Mount Vernon.
This required
rezoning of the area from Rl to R2, an item which was
apparently
not seen by
the surrounding
community nor
the
airport;
and
was
approved
by
the
zoning
board,
but disapproved by the City Planning Commission.
The airport attended several
of these hearings,
and
put
to
record
that
these
units,
if
built,
would
be
normally
unacceptable
for
multiple
or
single
family
residential
use.
And
if
one
nighttime
business
jet operation
was
added,
then
the proposed
site would
be
considered clearly unacceptable by the
Illinois Environmental Protection Agency....The units
have not been constructed;....IR.
3087.
The lack of effective airport zoning has contributed
to many
developments
in highly
noise impacted areas such
as new homes
in
a 73 Ldn area
(B.
3074) and new subdivisions near airport runways
(B.
1900—01).
A
director
of
the
Quad
City
Airport
testified
that:
the
last
subdivision
to
the
best
of
my
knowledge that has been developed
is southwest of the
airport
in the hills.
The heavy hill area.
There
is
another
one
in process
that will
also
lie southwest
from there....
Those
subdivisions
are
in
the
hills
among
the
trees
southwest
of
the
runway
the
elevation
is
approximately 100 foot higher than the
runway at that
point
R.
1900—01.
At Decatur Airport
a new residential development and a new
junior high school have been built.
An attorney representing the
Decatur Park District, owner and operator of Decatur Airport,
testified that:
tihe
nearest
concentrated
residential
development
to
the
airport
is
on
the
west
side
thereof,
approximately,
1,500
feet
from
the
north/south
runway.
Within
the development
on
the
west
side,
there
is
a
relatively
new
junior
high
school,
which school
is approximately 2,000 feet west
of
the
north/south
runway.
This
high
school
was
constructed
approximately
three
to
four
years
ago...Also
there
is
a sprinkling of new residential
69.126

—63—
development
approximately
3,000
feet
north
of
the
north
runway.
Airport operators uniformly suggested that there be
requirements for zoning that would allow the noise corridors to
be protected from incompatible developments.
A major problem
occurs where
a number
of governmental entities with zoning powers
exist around
the same airport
(B.
1900—02, 6281—3).
A director
at Quad City Airport further testified that:
tb
keep
track
of
all
the
zoning
changes
we
would
end
up dealing
with
the
city
of
Rock
Island,
the
city
of
Moline,
the
city
of
East
Moline,
the
village
of Cole Valley, the village of Milton and the
county of Rock Island.
R.
1900.
The Chairman of the Board of the Greater Rockford Airport
Authority provided
a possible solution:
tihe
more
comprehensive
solution
would
grant
airports
specific
zoning
power
over
the
property
around
them and would
mandate consideration of noise
impact when zoning.
R.
1330.
The Senior Vice—President of Operations and Airports
of the
ATA provided another possible solution:
Legislation
or
regulation
should
be
adopted
which
would
facilitate
and
indeed
require
multiple
communities surrounding
an
airport,
each
of which
is
now
a
separate political
entity,
to
act
as
a single
unit
or
as
a single political entity
in establishing
compatible
land
uses
in
areas
directly
impacted
by
aircraft noise.
ER.
3099
In response to
a question as
to how many jurisdictions are
involved in land use planning for areas impacted by 65 Ldn or
greater
from operations at O’Hare, Tiedt testified for the City
of Chicago that:
Eapproximately
45 communities and two counties,
DuPage
and
Cook
County,
each
of
which
possess
the
authority
to
regulate
land
use,
are
located
in
the
vicinity
of O’Hare.
ER.
6281—2.
She also testified that “twenty
communities,
including the
City of Chicago,
are included
in the area affected by aviation
activity
at Midway according
to the noise contours
in the
E1974
FAA study.”
(R.
6283).
Tiedt stated that the only municipality
to respond to the
noise problem with
a zoning ordinance against noise
is Elk Grove
Village
(R.
6244).
She said the MANAPS study concluded that
“reluctance
to give up control of land at the local level
‘is
69-127

—64—
the biggest obstacle
to regional land use controls around O’Hare”
(B.
6235).
MANAPS also recommended that
the Illinois Zoning Laws
Study Commission give further study to regional or
state land use
controls around airports.
Tiedt pointed out that:
Coincidentally,
perhaps,
many
of
the
most
vocal
proponents
of
the
regulatory
noise
controls
on
the
airport
operator
are
public
officials
in
those
communities
particularly
to
the
north
and northeast
of
the
airport,
in
which
failure
to
exercise
basic
compatible
land
development
control
is
evident
6246.
Under
cross
examination, however, Tiedt admitted that noise
contours which are useful
in planning development around airports
were not readily available before 1971.
Thus,
a community had to
rely on logic and
a knowledge of airport development
to plan
intelligently
ER.
6480
Even when local officials attempt
to plan for noise impacts,
they often have difficulty obtaining information necessary for
land use planning from airport proprietors.
For example,
representatives
of Des Plaines
(R.
317)
and Park Ridge
(R.
183)
testified
in 1977 that
they had been unable to obtain the O’Hare
Master Plan.
Studholme gave two reasons why proprietors are
reluctant
to release noise data to local communities:
For
the
proprietor,
when
he
does
do
a
noise
abatement
assessment
and
he
uses what
we
call
noise
contours,
he
really
encounters
two
very
curious
problems....
One
is
if
he
faces
litigation
or
any
kind
of
adverse
situation,
he
is
not
going
to
want
to
disclose that information at all.
It’s going
to be
a
very surreptitious
kind
of
activity,
he
is
going
to
want
to
know
what
the
noise
environment
around
his
airport looks
like, maybe
for land acquisition, maybe
to try
to seek
to really optimize his operation so he
doesn’t
create
much
of
a
problem.
But,
he doesn’t
want
to
show
that
to
the
local
land
use
decision
makers because there is
a great code of ethics
in the
Court
of Law....
The
second
area
that constrains
the
proprietor
in the use
of contours
is
that if he were
to disclose
this
information
and
show
it
for
some
future
time
frame
——
five years
or
ten years
from now,
he would
be
almost
in
a position of stipulating
that that was
the way
that
his
airport was
going
to
operate.
If
somebody
was
going
to
base
land—use
decisions,
hardnosed day
to
day land—use decisions——zoning,
and
the
improvement
of
the
construction
for
community
facilities
on
his
information,
then
he
would
69.128

—65—
basically
be
stipulating
this
is
the
way
my
airport
will
look
now
and
this
is
the
way
it
will
look
environmentally two years from now and ten years from
now.
In
many
cases
they
are
not
willing
to
put
themselves
in
the
position
of
not
having
the
flexibility
in the future;... ER.
2354—6
The MANAPS study also pointed out that continually changing
airport master plans can make
it difficult for local authorities
to plan around airports:
Any survey
of
planning activities
in the O’Hare
area
must
consider
the
significance
of
previous
airport master
planning efforts.
The airport master
plan more than any
single vehicle offers communities
in the airport environs a basis for their coordinated
planning
and
development
control.
The
alignment,
length
and
capacity
of
any
given
runway
have
an
important
bearing
on
runway
utilization
and
on
the
aircraft
noise
pattern.
Major
shifts
in
runway
alignments can have
a
significant
impact on planning
and development control
in the airport environs.
Due
to
a
number
of major modifications
in airport master
plans
since
1947,
communities
and
individuals
in the
airport
area
may
have
become
discouraged
in
their
efforts
to
plan
and
control
development
with
the
airport
in mind....It
is
obvious that the net
result
of
the
numerous
changes
that
have
occurred
in
the
airport
master
plans
has
been
the
confusion
of
individuals
and
government
officials
in
the
O’Hare
environs.
If
all
of
the
airport
plans
were
superimposed
the
result
would
be
to
bring
an
area
five
to
eight miles
in
radius
from O’Hare
under the
threat of serious noise impact
Exh.
223 B—l,
471.
Mr. John Tyler, who has
a degree
in mechanical engineering
and
is President of Aviation Systems Incorporated, discussed the
problems local governments face when proprietors can change
operations at will:
Well,
certainly
if
the airport operator has the
option
of
changing
ground
tract
at
will,
then
the
community
around
the
airport
is absolutely
helpless
because
the
community
may
zone
one
area
for
residential
and
another
for
manufacturing
and
have
the airplanes going over the manufacturing areas
this
year
and
next
year
suddenly
find
the
airplanes
are
going over the residential
area.
B.
1229
Clearly,
airport noise has
a significant impact on those who
reside near airports.
It
is also clear
that local land use
planners have failed to plan adequately for noise impacts
in some
instances and been thwarted
in their attempts
in others.
Airport
noise can be reduced
through a variety of methods which will
be
69-129

—66—
discussed infra, however, before going further
it
is necessary to
determine
to what level noise must be reduced
to be acceptable.
65 LDN STANDARD
The Attorney General proposes that
a standard of 65 Ldn be
established
for airport noise reaching Class A land.
Before
adopting this standard,
the Board must determine at what level
noise creates
a public nuisance which unreasonably interferes
with the general welfare of
the public.
This determination
includes consideration of physical and psychological effects as
well
as impacts
on business and recreational activities and
the
general quality of the environment.
Before considering the
acceptability of
65 Ldn as
a standard,
it
is necessary,
as
a
preliminary matter
to discuss how sound is measured and modelled.
Sound Measurement and Prediction
The proposal sets
a standard for noise emissions from public
airports to Class A land.
The standard
is expressed in terms
of
day/night sound equivalent levels computed from A—weighted sound
intensity levels
in decibels.
Sound
intensity
is measured
as decibels with respect to a
reference root mean square pressure
of 0.00002 pascals.
An A—
weighted network
is used to correct for the ear’s differing
perceptions of noise levels at different frequencies.
A—weighted
decibels are called “dBA’s”.
There are two methods of averaging variable dBA’s:
the
sound equivalent
level,
or “Leq”,
and the day/night sound
equivalent
level,
or “Ldn”.
The latter
is used
in the
proposal.
However, since Leq
is used
in this discussion, and
since
it
is conceptually simpler,
it will
be described before the
Ldn.
An Leq can be computed over any
interval.
In this Opinion,
unless otherwise specified,
“Leq” will
be taken
to mean an Leq
computed over
a 24—hour interval.
The 24—hour Leq
of
a variable
noise
is the dBA level of
a constant sound,
lasting
24 hours,
with the same energy
as the variable noise.
To compute a 24—hour Leq, one divides the day into “n”
different time intervals.
One then measures the dBA level
at
some point during each interval, and attributes this dBA
to the
entire interval.
An estimate
of the 24—hour Leq
is computed as
follows, where Li
is the ciBA measured
in interval
i,
lasting
ti
seconds:
n
Li/lO
Leq
=
—49.4
+lolog ~
(ti)l0
i=1
69.130

—67—
The estimate of Leg becomes more accurate as
the number
of
intervals increases.
Instruments are available which sample
essentially constantly, and which provide
a direct readout of
Leg.
The Ldn
is closely related to the 24—hour Leg.
The only
difference
is that
a
10 dBA penalty
is added
to any noise
level
measured at night,
in order
to reflect the greater impact of
night noise on the receiving population.
“Nighttime”
is defined
as
the hours of
10 p.m.
through
7 a.m.
Alternatively, and
equivalently,
any one nighttime noise event
is counted as ten
equal
noise events.
For example,
under
the Leg system,
if there were 90 day and
10 night operations,
the Leg value would be computed on 100
operations.
Using
the same hypothetical situation under
the Ldn
system,
the Ldn value would
be computed on 190 operations.
The
190 figure
is
obtained by multiplying each
of the
10 night
operations
by a factor
of ten and adding the resulting sum to the
90 day operation figure.
(S.
288—91).
It
is important
to understand how the sound expressed in Ldn
varies with the number
of operations.
If
55 Ldn
is
reached by
one operation,
65 Ldn will
be reached by ten and 75 Ldn by 100
similar operations
(R.
940).
A doubling
of the number of sources
will cause an increase of
3
dB.
Likewise
to decrease an Ldn
contour by
3 dB requires
a
50 percent reduction
in the number
of
sources
(B. 1097).
Thus
if 1,000 operations result
in 80 Ldn,
a
reduction to approximately 35 operations would
be
required
to
reach 65 Ldn
(R. 1100).
These estimates assume that day and
night operations have been cut
in a certain proportion.
An
operator could actually achieve greater reductions by cutting
nighttime operations preferentially.
Furthermore,
since
operations actually vary widely
in noise impacts,
an operator
could achieve greater reductions by eliminating the noisiest
operations.
The Ldn can be computed as follows, where L
is the
ciBA
measured
in
a daytime interval,
“td”,
or
a nighttime interval,
“tn”,
in seconds.
D
Ld/lO
N
Ln/lO
Ldn
=
—49.4
+
lolog( ~
(td)lO
+
10 ~
(tn)lO
d=l
n=1
The noise
at a given point produced by an aircraft operation
typically is variable and lasts several seconds.
This variable
noise level
is converted
to a one second Leg, called an “SEL”,
for use
in computing the Ldn at the point.
The SEL
is the dBA
level of a constant sound lasting one—second which has the same
energy as the variable noise over the length of time
it
persists.
Because aircraft noise events usually last more than
one second,
the SEL
is usually greater than the actual maximum
ciBA level achieved by the operation.
Exhibit
61 consists of
a
69.131

—68—
collection of charts which display the SEL at various points
in
front of and
to the side of the runway from various aircraft and
operations.
The SEL charts can be used to predict Ldn levels from
aircraft operations at points around an airport.
Since the
noises have been converted to a common one—second interval
in
computing the SEL, application of the Ldn formula becomes
a
matter of counting the number
of operations of each
type.
Formulas and
a systematic procedure are set forth in Exhibit
61.
Computer software
is
available to perform these
calculations.
Ideally the output is
a contour map of Ldn levels
predicted around the airport.
This
is called a “footprint”,
because the contours from a single
runway often look like
a
footprint.
Several noise descriptors other than Leq and Ldn are
mentioned in the record.
One of the most common is the Noise
Exposure Forecast referred to as NEF which
is used to predict the
noise impact on people.
NEF contours can be developed around
airports
in
a manner similar
to Ldn contours.
The scale
difference between Ldn and NEF is
35.
In other words,
a level
of
30 on the NEF scale
is equivalent
to 65 Ldn, and 40 NEF
is equal
to 75 Ldn
(R.
513—14).
The Composite Noise Rating (CNR), Noise Pollution Level
(NPL),
and Community Noise Equivalent Level
(CNEL) are other
descriptors.
An approximate
rule of thumb is that Ldn
is
approximately equal
to CNEL, which
is approximately equal to NEF
plus
35
which
is approximately equal to CNR minus
35
(Exh.
32,
p.
28).
SENEL is the Single Event Noise Equivalent Level.
The Acceptability
of 65 Ldn As
a Standard
The Ldn levels from
a variety of locations have been
documented and some of that data
is useful
to gain
a perspective
on the descriptor.
A tomato field
in
a California farm has an
Ldn of 44,
a wooded residential area
in San Diego 51,
a Boston
row house on a major avenue
68, downtown Los Angeles with some
construction activity 79,
and a third floor Los Angeles apartment
next to
a freeway has an Ldn of about 88.
Normal suburban
residential areas have an Ldn of about
55, while urban
residential areas have an Ldn of about
60
(Exh.
40).
A 1985
FAA
report,
entitled Aviation Noise_Effects discusses
the advantages of
using
the Ldn metric, which
it referred
to as
“DNL”,
as the noise
indicator:
While
a
dialogue
continues
within
research
circles
concerning
weighting
functions,
the
DNL
has
emerged
as
a
sound
and workable tool
for use
in land
use
planning
and
in
relating
aircraft
noise
to
community reaction.
The substantiating basis
for the
DNL can perhaps best be summarized
as follows:
69.132

—69—
1)
Pragmatically speaking,
it works.
Engineers and
planners
have
acquired
over
30
years
working
experience
with
a
nominal
10
dB nighttime weighting
function.
This
experience
has
been
successful,
contributing
to wise zoning and planning decisions.
2)
The
nominal
10
dB
ambient
noise
levels
in many
residential
areas
at
nighttime
provides
a
sensible
basis
for
the weighting factor.
(p.
15).
After
fifteen
years
of
use,
the DNL
has
shown
itself
to
be
a
workable
tool
for
the
noise
community.
Its use
as
the accepted measure
in time
of
day considerations,
with
its nighttime penalty
of
10
dB
between
10
p.m.
and
7
a.m.,
will
continue
unless
future
research
can
suggest
a
reasonable
alternative.
(p. 85).
The document also reviewed the recommendations and findings
of other agencies concerning
the levels at which noise becomes
unacceptable.
The Department of Defense discussion included the
following:
The
Department
of
Defense
has
also developed
a
comprehensive program
to minimize the harmful effects
of
aircraft
noise
(Ref.
4).
The
Air
Installation
Compatible
Use
Zones
(AICUZ)
program
requires
that
all
military
installations
be
studied
in
depth
to
determine
those
land
areas which should be specially
considered
in development
because
they
are
affected
by
aircraft
noise
(the
AICUZ
program also considers
bow
susceptible
an
area
is
to
aircraft accidents
in
its
compatibility
decisions).
This
system
is
also
based
on the DNL metric.
The AICUZ noise
zones and their compatibility with
development are presented in Table PP.
Regarding the policy of the Department of Housing and Urban
Development the report said:
The purpose of the BUD regulations
is
to protect
individuals
from
noise
in
their
communities
and
places
of
residence.
Basically,
BUD
policy
states
that BUD
assistance
is prohibited
for projects with
“Unacceptable” noise exposures
(noise levels above
75
dB
(DNL)
and
is
discouraged
for
projects
with
“Normally Unacceptable” noise exposures
(i.e.
a noise
level
above
65
dB
but
under
75
dB).
These
noise
levels
take
into
account
noise
from
highways,
railroads, and aircraft.
(P. 97).
S
69.133

—70—
TABLE PP
AICUZ Noise
Zones and Response
NOISE
ZONE
DNL
RESPONSE
3
Greater
Zone of highest
intensity; frequency and
than 75
cIBA
intensity of noise
is such as to
be loud
and annoying.
(Inhabitants may complain
repeatedly and even form groups to
protest).
2
65—75 dBA
Second most intensive zone;
noise
is more
moderate
in character.
(Inhabitants may
complain vigorously and concerted group
action is
a possibility).
1
Less than
Lowest noise
level
zone;
the noise may,
65 dBA
however, interfere occasionally with
certain activities
of the residents.
(pp.95—97).
Source:
Exhibit 229,
p.
97.
The FAA land use table
is reproduced on page
96
of the
report.
It lists various land uses with respect to their
suitability
at various
noise levels expressed
as Ldn.
All listed
uses are “compatible” at less
than 65.
Between 65 and 70 most
residential and school uses are “not compatible and should
be
prohibited.”
Between 70 and 75 various public and commercial
uses including nature exhibits and zoos are not recommended.
Above
75 almost all uses other
than
a few commercial and
manufacturing uses are “not compatible” or
require special design
or construction measures.
The report also recognized that sleep interference
(P.
51),
annoyance
(P.
26) and speech interference
(P.
43)
can result from
exposure
to aircraft noise.
The researchers reached several
conclusions regarding the direct impact of airport noise on human
health:
The E~pje in
a community surrounding
an airport
are
in
no
danger
(under
normal
circumstances)
of
hearing damage due
to aircraft noise.
(P.
42).
Although
many
airport
neighbors
have claimed
a
direct
health
impact
from aviation
noise,
there
is
little
valid
scientific
basis
for
such
claims.
(P.
61).
The
1971 Metropolitan Aircraft Noise Abatement Policy Study
69-134

—71—
for O’Hare
(Exh.
223 B—l)
recognized
30 and 40 NEF
(Noise
Exposure Forecast)
levels as adversely affecting certain land
uses.
These levels correspond to the
65 and 75 Ldn levels used
by the O’Hare Noise Abatement office.
The authors
of the study
stated that:
the
65—75
Ldn
contours
depict
areas
where
residential
land
uses
are
considered
‘normally
unacceptable’
by
standards
established
by
the
Department of Housing and Urban Development
(BUD) and
the
FAA.
The
75
Ldn
and
greater
noise
contour
represents
areas
where
residential
uses
are
considered
‘clearly
unacceptable’
by
the
federal
government.
(Exh.
240,
at 8).
The 1976 FAA Aviation Noise Abatement Policy
(Exh.
13)
made
the following statement regarding the effect of noise on people:
Aircraft noise disturbs the normal activities of
airport
neighbors
——
their
conversation,
sleep,
and
relaxation
——
and
degrades
their
quality
of
life.
Depending
on
the
use
of
land
contiguous
to
an
airport,
noise
may
also
affect
education,
health
services, and other public activities.
Although there may be indirect and subtle social
and
psychological
harms,
aircraft
noise
is
predominantly
an
annoyance
problem.
It
does
not
present any direct physical health danger
to the vast
majority of people exposed.
Pursuant
to Section 5(a)
of the Federal Noise Control Act of
1972
(42 U.S.C.
4901 et seq.,
86 Stat.
1239)
a USEPA committee
looked
at what level would protect the public health,
safety and
welfare with “an adequate margin of safety”
(B.
828).
It
interpreted that phrase
to mean “with no permanent damage
to
the
human bodily function” which
in turn means without any permanent
threshold shift on the human ear
(B.
829—30).
The USEPA Committee found that 96 percent of the population
would be protected with
an adequate margin
of safety from hearing
loss with an Leg value of 70 dB(A)
per 24 hours
(Exh.
40 at 3).
Dr. Von Gierke,
a member of
the USEPA committee who has a
doctorate
in engineering, agreed with that finding at hearing
(R.
825;
Exh. 32
at
33—4,
B.
684).
The committee also found that noise levels over
55 Leq
(24
hour) would
interfere with outdoor activity and people would be
annoyed
(Exh.
40 at
3, Exh.
32 at
34,
R.
840).
Indoor activity
interference and annoyance occurs at 45 dB
(24 hour Leg and Ldn).
Id.
It should
be remembered that in the case of airport noise
a
given Leg often reflects
a higher noise
level
than an Ldn because
the latter has a nighttime penalty.
69-135

—72—
The committee reported
that at
55 Ldn people generally
experience 100 percent sentence intelligibility indoors and 95
percent sentence
intelligibility outdoors.
At this
level
there
is no average adverse community reaction
to noise and while
17
percent of the population expresses some annoyance, only one
percent register complaints
(Exh.
40
at
23).
The level
of
annoyance rises with the noise level
and is due
to interference
with such activities
as speaking, listening
to the television or
radio,
sleeping,
and with vibrations
in buildings.
Dr. Henning Edgar Von Gierke, who has a Ph.D.
in engineering
and is director of the Biodynamics and Bioenergy Division of the
Aerospace Medical Research Laboratory of the U.S. Air Force at
Wright—Patterson Air Force Base
in Ohio, and who
is also one of
the authors of the study commented on
it in his testimony:
We
stayed
with
the
Noise
Control
Act
specification that we should
specify a level with an
adequate
margin
of
safety,
below
which
the
noise
would
have
no
effect
on
the
public
health
and
welfare,
we
said
that
55
Ldn
is
probably
this
level.
Below
this,
you
have
considerably
no
effect.
Above
this,
you
slowly
start
to
get
an
effect
and
probably
from
65
on
you
have
a
marked
effect.
And
as
we
stated
in
another
study
for
the
EPA,
above
75
is really the exposure area where once
you try to do something about
it as soon as possible.
B.
844.
Dr. Von Gierke testified that approximately
95 million
Americans are exposed
to Ldn levels below 55 decibels,
71 million
to between
55 and 65 Ldn, 31 million
to between 65 and 75 Ldn,
and 3.7 million
to more
than 75 Ldn
(B.
846).
He also said that
based on
a number of
surveys
it has been determined that at 55
Ldn approximately 18 percent of the population
is highly annoyed
while at
65 Ldn that figure increases
to
30 percent
(R.
942).
In a separate paper
(Exh.
32), Dr. Von Gierke reported the
results of
some of his studies of noise impacts:
As
for
speech
communication,
the
following
approach was taken
to quantify the noninterference of
environmental noise with speech:
indoors,
in private
homes,
100
sentence
intelligibility
is required
for
relaxed conversation
in typical
living rooms
for all
talker—to—listener
separation
distances.
This
is
achieved
for
Leg
less
than
or
equal
to
45
dB....Outdoors
95
sentence
intelligibility
appears
to allow
for
adequate,
reliable speech communication
for
people
who
are
walking
or
standing
close
together,
approximately
1
to
2
meters
apart.
Such
conversation
is
possible
in
noise
levels
up
to
approximately
60
dB steady A—weighted
sound pressure
level.
Noise
levels
at
this
magnitude
are
also
69-136

—73—
consistent
with
the
desire
for
speech
privacy,
an
attribute easily lost in the urban environment should
background noise
levels be too low.
This sound
level
of
60
dB outside (with
the average noise
reduction of
houses with partially opened windows assumed
to be
15
dB)
results
in
indoor
levels
of
45
dB,
the
same
levels
identified
for
satisfactory
indoor
conditions.
Therefore,
the
same
outdoor
level
satisfies
both
the
outdoor
and
indoor
speech
communication criteria....
When
the attitude
of people
toward
their
living
area
was
studied
and
their
reasons
for
desiring
to
move
away were
explored,
noise
did
not
represent
a
significant
factor
until
environmental
noise
levels
exceeded Ldn 55 dB....
Studholme,
testified that
“a
standard based only on health
and welfare, not considering any economic constraints or
technical constraints, would be exactly as the EPA specified,
which
is
55 Ldn.”
(R. 2421).
Dr. Galloway,
however,
a noise expert and witness for the
Attorney General,
testified that 55 Ldn was impractical
and that
65 Ldn is
a reasonable and desirable noise
level
to protect the
public health, safety and welfare
(R.
5383—86).
The testimony of the citizens at hearing strongly buttresses
the conclusion of the above
cited reports and witnesses regarding
the ability of airport noise to disrupt normal routines.
Although many specific comments were quoted earlier
in this
opinion, they will be summarized here:
Numerous people complained of sleep interference or
difficulty
in sleeping
(R.
266,
450—1, 719, 1010—11,
5024,
5060,
6569—71) and headaches and nervousness
(R.
327,
1521—3,
5060,
5859).
People complained of difficulty in talking intelligibly
outside or
inside when the windows are open,
talking on the
telephone,
listening
to television,
and using the backyard or
patio
(R.
424, 705, 711,
719, 741, 969—70, 1002,
1010—11,
1042,
2986, 4349).
There are reports of structural damage such
as
broken and rattling windows,
ceiling cracks, and vibrations
to
homes around O’Hare
(R.
6566—69, 6665,
5043—4).
Two people
testified that they wear headphones around the house
(R.
1039—
5043).
Communication interference occurs not only at home,
but also
at school
(R.
5075—6,
4235 et seq.)
It has been termed the “jet
pause syndrome” or the “Bensenville syndrome”
(R.
388,
284,
288)
and
is especially prevalent during warm weather when windows are
open.
One school still experiences the problem even when forced
to keep its windows shut
(R.
5857—8).
A student from this school
implored that someone stop the noise because the students and
teachers have difficulty
in hearing each other.
Id.
A teacher
69.137

—74—
from another school stated that on certain days she loses
five to
twenty minutes of classtime per class due
to the jet pause
syndrome
(R.
392).
Another loses thirty seconds per flight
(R.
6573).
A school superintendent states that although there
is no
precise measure of the
interference to the educational process of
a child, that nonetheless it
is happening
(R.
284—5).
In an
informal survey high school teachers
at one high school were
asked what percent of the time classes were halted due
to jet
noise.
Twenty—one responded one to five percent while eight said
six
to eight percent of
the time
(R.
286).
When asked what
percent of the time does jet noise
cause a loss of effectiveness
in class proceedings without halting activities, eleven responded
one to five percent while five said from six to
ten percent.
Id.
Another informal survey elicited written student and teacher
responses some of which were read into the record.
One student
commented that the noise
is annoying and that class has
to stop
every sixty seconds
(R. 6574).
Teachers responded that slow
learners, special
education children, bilingual children and
children with weak concentration skills are especially impacted
by the noise
(R.
6574—6).
During
the supplemental hearings of September 1985,
a
doctoral dissertation was submitted as Exhibit 235A by Dr.
Kenneth
L. Kaufman, Assistant Supeintendent of Schools
in
Bensenville, entitled “An Investigation of Teacher Voice Signal
Amplification Treatment for Mediating Speech Communication
Interference from Jet Aircraft Noise Intrusion and from Minimal
Hearing Loss
in First and Second Grade Classrooms”.
In the
study, classroom teacher voice amplification was evaluated
to
assess
its effect
in overcoming
two suspected forms of speech
communication interference:
jet aircraft noise intrusion
(JANI)
arid minimal hearing loss
(MHL).
Voice amplification was successful
in raising students test
scores.
Those
in the group with amplification did significantly
better on standardized tests than the group without
amplification,
“with significant differences occurring
in the
linguistic subskill
tasks of phonics—consonants, auditory
discrimination and phonetic analysis”
(Exh.
235A).
In auditory
discrimination,
test results for the amplification group exceeded
those of the control group comparable
to one year and one month
in grade
level equivalents while
in phonetic analysis,
the
difference was five months.
Id.
It must be pointed out that the Kaufman study did not
associate airport noise as a substantial contributor
to MHL;
attempts to do so were inconclusive
(S. 144—6).
Dr.
Kaufman,
however, suggests that JANI
is worse on first and second graders
(S.
137).
Reduced to costs,
the study predicts that with
MilL children,
educational
costs rose because of MHL children’s need for special
tutoring and the frequent misdiagnosis of MHL children as special
educational students
(S.
154).
Therefore,
there
is a loss of
69-138

—75—
teacher time and it
takes more teacher time per learning unit
(S.
157—8).
Both the insulation of schools and the installation of
air conditioning units causes increased costs
to all
involved
(S.
158—9).
Several witnesses testified regarding possible health
effects of airport noise.
While testifying
in answer
to a
question, Dr. Galloway stated that he was not aware of
physiological damage resulting from aircraft noise:
If
one
means
“physiological
damage,”
a
measurable
physiological
change
such
as
hearing
impairment
——
to
my
knowledge,
no
such
situation
exists around commercial airports.
There
have
been
some
instances
in
the past
at
some
military
installations
where
there
have
been
some claims of having some impairment of hearing as
a
result
of
airport
noise
involved
with
airport
operations.
I
do
not
believe
in
the
case
of
any
commercial,
civil
airport
operations,
there
is
any
evidence of literal physiological damage....
You
asked
about
studies.
This
is
not
to
say
that
there may
not be
some long—term effects
in some
high—noise
areas
where
residents may
be exposed
for
very long times.
But
I don’t know of any evidence
to
show that is so.
That’s all
I can say.
(R.
5472).
However, one Bensenville resident stated:
I personally feel that
I have suffered some loss
of
hearing
as
a
result
of
living
amid
this
noise
pollution.
I
believe
careful
study
would
show
this
to be true for many of us who live here
(R.
6584).
An otorhinolaryngologist,
based on his knowledge of
the
literature, testified as
to the general health effects
of
noise.
He stated that over
80 dB damages the inner ear cells and
that there would
be
an irreversible hearing loss
(R.
5243).
This
condition becomes more pronounced after repeated exposure.
Id.
Besides hearing loss (called “acoustic trauma”), he testified as
to noise interference
in relation
to sleep.
Loud noise disturbs
brain activity (determined by electroencephalograph recordings)
and the rapid eye movement (REM) phase
of sleep
(R.
5233).
Furthermore,
based on a study of male workers
in industrial
plants,
there
is evidence that people subjected to loud noise
have increased blood pressure
(R.
5234).
Those with noise
induced hearing loss had with higher blood pressure than the
control group.
While this suggests a relationship to other
situations,
such as airport noise,
it
is not definitive and more
studies need
to be done.
The doctor mentioned other noise—
related effects such as glandular disturbances, coronary artery
disease, and fetal abnormalities
in rats
(R.
5234—9).
69-139

—76—
It
is well established
in the record that the Ldn metric
is
a
reasonable measure of aircraft noise and its impact on people,
that
it
is widely used by government agencies for that purpose
and that
it will be
in use for the foreseeable future.
The
testimony of residents near airports confirmed the predictions of
the experts and exhibits regarding the impact of noise on daily
life.
The proposed 65
Ldri
standard for the protection of the
public
is reasonable especially
in light of the testimony
supporting an even tighter standard based solely on health and
welfare.
The Board
finds that 65 Ldn
is
an appropriate standard
for
purposes of controlling airport noise.
The technical feasibility
and economic reasonableness of such a standard will
be discussed
in following sections.
NOISE MODELLING AND MONITORING
The noise standards proposed
in Section 904. Subpart B are
based on annual averages.
A data collection and reporting
program
is established within Section 904.301.
Pursuant to this
section the proprietor must record and report all information
needed
to run the FAA Integrated Noise Model
(INM) described
in
Exhibits 254 and 255.
By way of example, such information would
include data on runways,
ground tracks, approach profiles and
runway utilization and number of operations.
This data will
be
used to develop noise exposure maps and for enforcement
purposes.
The Attorney General’s original proposed rule 504 had
been amended, possibly to avoid the Illinois Environmental
Protection Agency’s
(Agency) position that stage length, aircraft
number and type was insufficient for computer modelling
(R.
5408).
As originally proposed, Subpart B
(proposed rule 503) simply
stated the noise standards,
but did not specify whether they were
daily or annual averages.
This ambiguity was
noted
in the
hearings
(R.
2590—2600, Exhibit 112).
If the appropriate
standard
is
based on an annual average, then exceeding
the
standard on one day will not subject the proprietor
to a
violation of the annual average
(R.
2479—80, 2594—6).
Because
the proposed language did not specify, one could assert that a
proprietor could be found
in violation
of the standard based on
data for one day
(R.
2590—2600, Exhibit 112).
The Board,
however, believes that the ambiguity
in proposed rule 503
is
unacceptable.
Therefore,
the Board
is amending it
to specify
standards based
on an annual average
as the 365 day average,
in
decibels, day/night average sound level
(See 14 CFR
150.07).
The Board believes that
a standard based on an annual average
is
amply supported by the record
(Exh.
61, 110).
Sound levels around
an airport will need
to be determined in
two instances.
The first
is for planning purposes wherein a
proprietor
needs
to know the sound
levels around an airport and
69-140

—77—
any sound level changes due to various operational changes.
The
second
is for enforcement by a third party of any adopted noise
standard.
Sound levels may either
be directly measured or
they may be
modelled.
Modelling
is accomplished by use of a computer
model.
The utility of models as planning tools was generally
acknowledged throughout the record.
There
is a dispute,
however,
as
to
the dse of models
in enforcement proceedings to enforce
noise standards.
The basis
for the dispute
is the question of
the accuracy of the models.
Additionally,
the participants
disagree
as
to how actual sound
level measurements should
be used
to determine violations.
Specifically, how many days of actual
measurement are needed
to show a statistically significant
violation of an annual Ldn average and at what confidence
level.
Many witnesses testified concerning these problems,
especially for the ATA,
the Attorney General’s Office,
the City
of Chicago, and the Illinois Environmental Protection Agency.
When determining how
to measure sound,
three key concepts
need
to be understood.
The first concept
is the measurement
tolerance or accuracy of
the equipment to be used.
For example,
at Capital Airport,
the decibel noise meter was calibrated to
record noise within plus
or minus one decibel
(March 11,
1980,
transcript at
40).
Second, confidence
intervals must be
chosen to reflect the
degree of accuracy wanted.
At a
90 percent confidence
interval,
if 100 samples are collected,
90
of them on the average will
be
within the interval
(Exh.
223 (C—l) at 2—10).
Mr. Robert D.
Hellweg, manager of the Noise Technical Operations Section of the
Illinois Environmental Protection Agency who holds Bachelor and
Master degrees
in aeronautical and astronautical engineering,
testified concerning the accuracy of confidence intervals:
in
English terms,
it means
the
number
of data
points
increases
as
the
confidence
interval
increases.
If you want
to
be
99
percent
confident,
that
requires
more
data than
if you wanted
to
be
90
percent
confident.
The
number
of
data
points
increase with increased accuracy.
If
you wish
to
be
plus or minus
10 percent
you
would
require more data points than
if you wanted
to
be
plus
or
minus
25
percent.
Also,
the
number
of
data
points
would
increase
as
your
variance
increases;
that
is,
as
the
data
scatters
more,
one
must
have
more
data
points
to
have
an
accurate
estimate of
the mean value.
Unfortunately,
one
cannot
know
the
standard
deviation
of your data until you have measured.
One
cannot
know
before
you
go
out
to
measure what
the
standard
deviation
is,
that
is,
how
much
the
data
69.141

—78—
varies.
You
can
only
determine
this
from
measurements
March
11,
1980 transcript at 41—2.
The third concept
to be considered
is data independence.
If
the data points are statistically independent, fewer data are
required to achieve
a desired accuracy within
a specified
confidence interval than
if the data points were were
dependent.
Unfortunately, one does not know
if the data will
be
independent
until after measurements are taken.
Witnesses disagreed on several
aspects of data collection
and its usefullness.
The ATA witness considered Ldn as
a land
use planning tool only rather than an enforcement tool
(R.
3639).
An Agency witness stated that a 95 percent confidence
level should be used
in measuring
for enforcement purposes.
He
testified that to measure
a significant average annual Ldn at 95
percent confidence,
one would have to measure at the site for
85
days
(March
11,
1980 transcript at 51—5, Exh.
197 S—V—Y).
The City of Chicago witness testified that he would like
to
see 100 percent confidence
(R. 6505).
However,
a witness for the
Attorney General’s Office testified that:
Wjhen
measuring any kind
of
a dynamic process,
one
is
never
going
to
measure
the
average
value
of
that process correctly within one hundred percent or,
let’s
say,
zero percent error
as long as
the process
is
dynamic.
It’s
changing
all
the
time,
so
there
isn’t
any
way
one
can measure
the
precise
value
of
whatever this process
is
R.
5774).
Dr. Galloway suggested
the use of a
90 percent confidence
interval with
a tolerance level
of 1.5 decibels.
It has been
used previously by other regulatory agencies:
Well,
the
90
percent,
one—and—a—half
decibel
interval
that we
suggested
as
a possible use
in
this
regulation,
is
used,
for
example,
in
Part
36
to
determine
the
reliability
of
the
measurements
or
acceptability
of
the
measurements
in
the
certification process.
It’s also used
in some of the
foreign
certification
processes.
It’s
used
in
the
International
Civil
Aviation Organization,
ICAO
R.
5776—77).
The final problem
to be addressd
is data independence and
how it relates to the measurement of airport noise.
Heliweg
summed up the problem best when he testified:
Why
would
the
data
not
be
statistically
independent?
What does
that mean?
What
it means
is
that
the
measurements
we
take
today are
related
to
the measurements
or
the sounds that occurred the day
before.
69.142

—79—
How
could
this
happen
at
an
airport?
We
are
measuring sounds from distinct jets that occur
today;
the day before were different jets
that operated.
There
are
several
reasons why
the
data may
not
be
independent.
The
most
obvious
is
weather
conditions.
If
the
wind
is
blowing
from
the
west
today,
there
is
a
high probability
that
the winds would
be
blowing
from
the
west tomorrow
or
the day before and
wind factors and weather factors mean that operations
on
specific
runways
are
related
on
a
day—to—day
operation.
Other
factors
that
would
make
the
data
not
independent would
be the schedules
of aircraft.
On a
day—to-day
basis
——
airline
schedules
follow
a day—
to—day
basis
and
there
may
be
a
jet~scheduled
to
leave
at
11:00
o’clock
at
night
every
day
and
this
would
indicate
some
relationship
between
the
sound
levels
we
measured
today
to
the
sound
levels
that
were
the
day
before.
March
11,
1980
transcript
at
42, 43.
Regarding
the issue of how many days of measurement are
required
to determine
an accurate estimate of the annual
day,/riight sound
level,
another witness for
the Attorney General’s
Office, Studholme,
testified that on—site measurement of airport
noise on
a specific Class A parcel need only take two days
CR.
2512),
even though the engineering firm he
is employed with
recommends
at least two weeks of measurement
(R.
2514).
Hellweg testified that 85 days of measurements were needed based
on the statistical
accuracy of
31 days
of actual noise
measurements
at
a residence 4,000 feet from runway 4—22 at
Springfield’s Capital Airport
(See March 11,
1980 transcript at
30 and following; also Exh.
197,
198).
The data from Capital Airport were
run through the run test
and the trend test (Exh. 197)
to determine if they were
statistically independent.
Both tests showed
the data to be
statistically independent
at the 95 percent confidence interval
(Exh.
197
J,
K,
L,
and M).
When data is not statistically
independent
but
is dependent on prior
data, an autocorrelation
analysis
is performed on the data
(Exh. 197,
G,
H).
Hellweg then analyzed the data of 13
airports
in Exhibit 198
to see
if they were statistically independent.
The values at 12
of the
13 airports were found not to be statistically independent
(March
11, 1980 transcript
52—3,
Exh. l97S).
Therefore,
for the
data
to be statistically significant when measured on a
69-143

—80—
continuous basis,
the data would have to come from a larger
sample size of days measured.
While Heliweg’s statistical analysis
is in—depth,
it omitted
calculations at other confidence levels.
It further did not
include solutions as suggested by Dr.
Schomer and Mr. DeVor
to
the problems
of measuring airport noise.
In Exhibit 198,
which
data was used for further analysis by Heliweg, Dr. Schomer and
DeVor concluded that the high number of days needed for
continuous monitoring could
be reduced by measuring randomly,
thereby injecting more independence into the data:
Because
of
the
correlation
factor
generally
exhibited
in most
of
the noise series,
the number
of
sampling
days
can
be
significantly
reduced
by
inducing
randomness
in
the
selection
of
days
sampled.
That
is,
sample
days
can
be
selected
sufficiently
far
apart
to
induce
randomness
in
the
data
gathered,
rather
than
performing
continuous
monitoring
over the total number
of days.
Because
of
the
long—term seasonal
weather
effects
exhibited
in
some of these data,
it
is recommended that samples be
selected
from throughout
the entire
year.
A variety
of
strategies
can
be
employed
based
on
this
analysis.
For example, one could:
a.
Sample
for a continuous period of 30
to 60 days.
b.
Sample
14
days
chosen
randomly
throughout
the
year
(using different days of the week).
c.
Sample
for
4
one—week
periods
——
each
chosen
from
a different season.
The
above
can be
summarized
as
a recommendation
for
employing
14
days
of
totally
random
sampling
throughout
the
year,
or
four
weeks
of
quasi—random
sampling
taken one
week
at
a
time from each season,
or
eight
weeks
of
totally
continuous
sampling
to
achieve a precision of +2
to —3 dB of the true yearly
CNEL or Ldn at
a 95 percent level of confidence
Exh.
198 at 14, 15.
Therefore,
the lack of data independence, which causes the
number of monitoring days
to increase in the airport noise
measurement scheme,
is not a stumbling block
to the proposed
regulation.
The measurement method chosen,
if not continuous,
must inject enough independence
in the data so as
to
be
statistically significant at least the 90 percent confidence
level.
The firm of Bolt, Beranek
arid Newman, which reviewed the
AGO’s proposed rule commented on the variability problem as
follows:
69.144

—81—
Because of the
variability
in
airport operations and
in
individual
aircraft
noise
measurements,
repeated
measurements
of
either DNL
or
SEL
values
are needed
to
define
the
yearly
average
DNL
to
an
acceptable
level
of
precision.
However,
continuous
year—long
noise monitoring
is
not
required,
since
measurements
over
much
shorter
periods
of
time,
acquired
in
conjunction with airport operations information, will
permit
accurate
prediction
of
yearly—average
DNL
values.
Where
noise
monitoring
is
required
to
establish DNL
values
(see
Section
5)
it
is
recommended
that
field
measurements
be
made
to
achieve
a
90
confidence
interval
of ±1.5
dB.
This degree
of precision can
clearly
be
attained
within
reasonable
time
periods
(order
of
2
weeks)
provided
the
following
basic
operational
information
is obtained:
1)
The
number
of
operations
of
the
noise—
significant
aircraft,
and
runway
usage
during
the field measurements.
2)
Yearly—average
number
of
operations
of
noise—
significant
~ircraft;
and
the
yearly—average
runway usage.
The
above
operational
information
is
the
key
to
adjustment
of
monitoring
data
to
obtain
yearly—
average data of the desired precision
Exh.
217 at 57
and 58.
The next issue concerns the accuracy of models and their use
for enforcement purposes.
Objections
to the use
of models stems
from their
having certain “margins of error.”
One computer
model,
the FAA’s Integrated Noise Model
(INM) Version
I
(Exh.
110, Wyle Model),
is said to have an accuracy of plus
or minus
five decibels
(Exh.
110
at 1—10).
The INM itself provides that
“a
validation study of
the INM is currently in progress.
The
INM (or
any other method) cannot predict noise impacts with
pinpoint accuracy.
It
is anticipated that the observed values of
aircraft noise
in NEF, Leq,
Ldn, and CNEL will fall reliably
within
+/—
5 dB of the levels predicted.”
(Exh.
110 at 1—10).
One ATA witness, Richard
E. Coykendall, who has
a degree
in
mechanical engineering and
is an Aircraft Development Manager for
United Airlines, testified that
“I think they
the
FAA) have
clearly stated
it should not be
relied upon
to be more accurate
than plus or minus
5 dB.”
(R.
3641).
What this means is that “an
80 Ldn noise contour could possibly range from 85
to 75 Ldn and
a
65 Ldn could range from 60 to 70 Ldn.”
(R.
6470).
The impact of
a ±5decibel variation
is given
in the testimony
of Chicago.
At
O’Hare,
a
5 dB error on the 80 Ldn contour would overestimate
69-145

—82—
the impacted housing units
by 9,800 while a
+
5 dB error would
overestimate by 2,200 units
(Exh.
223,
III,
3).
The validation study of the INM generally shows
that the
accuracy of Version
I of the INM
(Exh.
110) differs by category
of aircraft.
In testimony regarding the validation study
(Exh.
223C—l), Mr. Holder
for the City of Chicago testified:
In the
case
of
two and three—engine narrow body
aircraft,
it
shows
that
the...difference
between
——
the
observation
and
the
noise
calculated
is
on
the
order
of minus
three
to zero decibels.
As
you
move
down
that
becomes
greater
in
the
four—engine
category,
in
the order
of five
to six to
seven decibels.
When questioned whether the validation study would
tend to
confirm or deny the plus
or minus five decibel accuracy of the
INM,
Holder testified that
“I would tend
to think
it would
confirm it.”
(R. 6531).
The Agency on cross—examination of Holder questioned his
conclusions on the accuracy of
the INM given that the
FAA
had
only examined the accuracy of individual categories of planes on
arrival and on departure.
What the Agency felt was necessary was
an average difference between observed noise level and INM
prediction based on the differences between observed
noise and
INM calculations for individual aircraft
(R.
6534,
6538—45).
The
Agency intimated that the accuracy of the INM was greater than
the
FAA
validation study
(Exh.
223C—l)
indicated
(R.
6537—8).
Nevertheless, even
if an accuracy
of plus or minus five
decibels for the INM
is assumed,
the issue becomes whether
it can
be used for enforcement purposes.
The Attorney General suggests
that the INM be used
for enforcement purposes
at a confidence
interval of
90 percent with
a tolerance level
of plus or minus
1.5 decibels
(AG Comments October
26,
1983 at
26).
The Attorney
General argues that when
a sound level exceeds the noise standard
over
and above
the plus
or minus 5dB error
of the INM,
then
a
violation
is proven.
Actual monitoring would not be needed.
If
a modelled violation was only five decibels above
the noise
standard, however, monitoring would
be needed to show the
violation because the modelled violation would
fall within the
INM margin of error.
EFFECTIVENESS AND PRACTICALITY OF NOISE REDUCTION METHODS
A large number
of steps can
be taken to reduce noise around
an airport.
The various methods will vary in their effect and
acceptability as well as their cost
at different airports.
This
section discusses
a variety of methods without implying that a
proprietor may unilaterally implement them.
Proprietors will
have
to individually assess the methods and determine which are
69.146

—83—
acceptable and legally permissible
at their facilities and
whether the FAA or some other agency must approve
implementation.
The Board anticipates that
a variety of methods
will be utilized.
It
is unrealistic
to assume that any one
method will solve
the problems at
a particular airport.
Retrofit, Replace and Re—engine
Individual planes can be quieted by retrofitting existing
engines with sound absorbing material
(SAM)
or making other
changes
to
the aircraft or engines.
A plane may also be
re—
engined with quieter engines.
Another option is
to retire older
aircraft and replace them with newer models.
General von Kann,
Senior Vice—President of Operations and Airports for the Air
Transport Association, stated that in terms of effective noise
reduction
it
is best to replace, re—engine,
and retrofit
in that
order
(R. July 27,
1978 at 3087—90).
Retrofitting reduces noise by
a
few decibels at relatively
low cost.
For example,
a DC—9 SAM retrofitcosts about $273,000
per plane while
a DC—8—61 SAM
retrofit runs $2.3 million.
To re—
engine the same planes would cost approximately four and ten
million dollars
respectively
(R. July
27,
1978,
at 3089—92).
Retrofitting often does not benefit fuel economy,
and
in some
cases
leads
to reduced fuel efficiency
(R.
3148).
On the other
hand,
replacing engines
or planes can lead to substantial fuel
savings.
For instance,
a re—engined DC—8 saves 10
to
15 percent
on fuel
(R.
3163),
while the new 767’s and A—300’s save 15
to
25
percent fuel compared
to older planes
(R.
3096).
Some individual
models,
however, are difficult to re—engine.
For example,
the
727 cannot be re—engined without a
tail redesign
(R.
3614).
As
to the
feasibility
of replacement, airlines are reluctant to
retire planes that are otherwise useable just because they are
noisy
(R.
5436).
The history of one company’s efforts
to come into compliance
with FAR Part
36 was provided by Flying Tigers,
an air freight
carrier.
During
the April
8,
1980 hearing,
a representative
described the different options available to
reduce the noise
emitted from its DC—8 aircraft fleet.
Retrofit per aircraft
in
1979 would have cost two million dollars and would have provided
a
33 percent reduction
in the noise footprint of the aircraft
(R.
4728).
Re—engining
in 1979 would have cost $11 million per
aircraft and would have provided a 90 percent reduction
in the
noise
footprint.
Id.
By public comment submitted on November
4,
1985, Flying Tigers informed the Board that
it has “replaced out
sic
entire DC—8
fleet with quieter, more fuel efficient 747’s
and 727’s within recent years and are
in 100
compliance with
Part 36 regulations”.
(Public Comment 131).
At the 1978 hearings, General von Kann gave the cost of
bringing the national fleet
into compliance with FAR
36
as about
seven and one half billion dollars
(R.
3092).
To place
this
in
the context of then current air service, he pointed out that a
69-147

—84—
two percent tax or surcharge on airline passengers would generate
about two billion dollars
(R.
3095).
By the time of the 1985 hearings,
89 percent of the
total
U.S. registered
fleet of jet aircraft was in compliance with FAR
Part
36
(Gr.
Exh.
231 at
2).
The remaining planes
received
exemptions which expire
in 1988.
The City of Chicago attributes
the decrease
in the overall size of
the 1984 65 Ldn contour at
O’Hare
to the airlines’
increased use of quieter aircraft
(Exh.
240,
contour map enclosure).
The success of airlines
in meeting Part
36 demonstrates that
technological advances
in aircraft design can help reduce airport
noise
levels.
In 1978, Tyler
testified that incentives are
necessary
to encourage
the development and purchase of quieter
aircraft.
He spoke of
the impact
the Port Authority of New York
had on aircraft design and procurement with its decision
to
establish limits on takeoff noise:
At that
time
I was
in
charge
of Noise Abatement
Research
and
Development
of
Pratt
and
Whitney
Aircraft, and
the establishment
of
that limit
by the
Port Authority of New York and New Jersey became the
target
which
our
customers
said must
be
met
by
the
next generation
of aircraft....
Now,
the
next
gener~ation are
going
to
be
significantly quieter
again due
to
again
an increase
in
bypass
ratio
and
the
use
of
sound
absorbing
material
and
all
of
the
other
technology
features
that
make
airplanes
quieter.
Our
problem
is
to
provide
incentives
for
airlines
to
buy
quieter
airplanes rather than noisy ones.
And
let me
just
say
that
the process
by
which
this
occurs
comes
in
negotiations
between
the
airlines
and
the
manufacturers
at
the
time
when
an
airplane
is
being
developed.
And,
I
have personal
experience
on this since
I was
in charge
of Aircraft
Noise
Abatement
at
Pratt
and
Whitney,
and
my
department
was
able
to
develop
noise
abatement
features
which
were
frequently
not
incorporated
in
the
engine
because
the
customer
felt
that
the
benefits were not worth
the cost....
And airlines like any other company,
if you make
it
desirable
from
their
standpoint
to
make
them
quieter they will make them quieter,
but
if they have
no incentive why spend an extra dime
ER.
1171—1179
Now,
during
the
period
following
the
implementation
of
the
original
Part
36
Noise
Regulations, there has been significant change in the
technology
and
as
I
mentioned
earlier,
we
are
just
69-148

—85—
very
fortunate
that
the
improvement
in
engine
performance
is
accompanied
by
a
reduction
in
noise.
These
two
go
hand
in
hand,
so
that
the
next
generation of aircraft could be significantly quieter
than
the
last
generation.
In
fact,
testimony
presented
before
the
Aviation
Subcommittee
last
spring
by
Pratt
&
Whitney
indicated...a
10
dB
reduction below
the
original Part
36 Requirement
R.
1231—32).
The chairman of the Bensenville Environmental Protection
Coalition made
a similar point
in
1985:
One means of encouraging
the development and the
purchase
of
new
improved
and
beneficial
aircraft
designs
and
engines
is
to
set
goals
in
the
form
of
standards
and
to
set
regulations
which
must
be
met.
Competition
between
manufacturers
or
(sic
aircraft
and
aircraft
engines
is
such
that
they
need
the
impetus of regulations
to be met.
I
was
at
a
recent meeting
for
the organization
NOISE,
and
one
of
the
engine
manufacturers
stated
very
plainly
competition
dictates
what
they
build,
and
they
are
building
quieter
aircraft
engines
largely
due
to
some
of
the
strict
standards
set
at
Washington
National.
I
think
that
is
very
important.
I
think
Illinois
should
be
setting
standards like that
S.
250—51).
Coykendall believed that noise emissions were already
considered
in aircraft purchase decisions:
T)he
recent
competition
we
had
between
the
Boeing
767
and
the
air
bus,
we
made
explicit
comparisons
between
the
so—called
guaranteed
noise
levels
of the airplanes.
The
extent
to
which
they were
expected
to
fall
below the
Stage
3
requirements
and
these
facts were
one
of
the
key points
of information provided
to our
executive
staff
for
their
evaluation
in
the overall
judgment of the airplanes.
So
I
think
that
it
is
totally
incorrect
to say
that
the
noise
requirements
are
not
part
of
the
consideration
in
the
acquisition
of
new
airplanes.
They
figure
very
heavily
and
are
receiving
quite
a
lot of attention
ER.
3824).
It was generally agreed
that while
it helps, new technology
will not solve the airport noise problem.
General von Kann
pointed out that hardware changes alone would
not solve
the noise
problems around airports, especially in the absence of land ~use
69-149

—86—
controls
(R. 3100).
A citizen stated,
“I question whether
the
quieter engines
in the new generation of aircraft
is a
satisfactory balance to more aircraft and more flight paths which
will impact more areas more frequently.”
(S. 250).
Takeoff and Landing Procedures
Operational procedures during takeoffs and landings can be
modified
to reduce
the level of noise emitted.
These procedures
emphasize controlling thrust and the drag caused by flaps,
since
noise is generated by the engines and airframe.
When and where
a
pilot applies
thrust has considerable influence on an individual
plane’s noise pattern.
A balance between thrust and flap
settings must be maintained because
as a practical matter both
cannot be reduced simultaneously,
especially on takeoff
(R.
3269).
An added benefit of reduced thrust
is
that it increases
engine life and reduces maintenance requirements
(R. 3247).
Captain H.B.
Benninghoff,
a pilot who
iS Assistant Vice
President of Flying
for America Airlines ana participated
in
numerous noise abatement tests,
discussed takeoff procedures.
He
pointed out that planes operate within a fairly narrow band of
operational choices
and must reach
a safe altitude before flaps
or thrust reduction occurs
(R.
3269).
After reaching
a safe
altitude:
You
can
either
leave,
takeoff
thrusts
on
the
engines
and
reduce
flaps
as
the
airplane
increases
speed,
maintaining
adequate
stall
speed
margin,
or
you can reduce thrust to some intervening setting and
leave
the
flaps
alone,
do
not
move
the
flaps
or
retract the flaps.
You cannot do both.
The airplane
needs
——
any
airplane
needs
a
certain
amount
of
thrust
for
the
drag
which
is
takeoff
flaps
in
this
case
(R.
3270
Other witnesses commented on the noise
impact of the two
takeoff procedures.
The rapid climb procedure calls
for rapid
acceleration until
the aircraft reaches zero flap at which point
there
is
a thrust cutback, usually occuring four miles
from
takoff
roll, which
is about two miles from the airport boundary
(R.
1102—03).
This procedure emphasizes speed rather than
initial climb,
although the aircraft
is continually increasing
in
altitude
(R.
1117—19).
The rapid climb produces more noise near
the airport;
but, once
a certain height is attained, there
is
a
thrust cutback,
reducing noise after a certain distance from the
airport.
In contrast,
the reduced thrust takeoff uses less than
full thrust from the beginning
(R.
155), which would tend
to emit
less noise closer to the airport than the rapid climb approach.
Benninghoff believes that “the benefit derived from takeoff
noise procedure change
is highly overrated.
There
is very little
there.”
(R. 3366).
He also feels that these procedures will do
little to benefit people living within three miles of the
runway
69-150

—87—
(R.
3284).
He also expressed concerns about safety
if takeoff
procedures were varied, stating that the ATA Flight Operations
Committee and pilots want
a single standard procedure.
He spoke
from the pilot’s point of view:
C)ompliance
with takeoff procedures
is based on
conformance
to
procedures
and
techniques
that
are
committed
to
memory.
There
are
no checklists
when
you
are
flying
an
airplane
in
terms
of
actual
manipulating
of
the
controls,
and
to
burden
pilots
with
a
multiple
number
of
takeoff
departures
would
create
a
concentration
problem
on
a
non—standard
situation,
which
creates
a
burden
in
terms
of
the
primary job of getting safely aloft
ER.
3340—41.
Benninghoff cited additional complicating factors in takeoff
such
as type of plane, weight, weather,
and ground obstacles
(R.
3333—41).
He also pointed out that different planes have
different climbing characteristics.
Thus any takeoff procedure
must take these factors into account
to prevent aircraft from
overtaking each other and violating departure separation
distances
(R. 3278).
Operational procedures during landings also may be modified
to reduce noise.
However aircraft vary
in their design
specifications and consequently, their performances are
different.
Varying thrust and flaps has some quieting effect,
but the distance required
to lihe up large planes on approach
limits the available options
(R.
3482).
Reduced flap landings
were ordered by the FAA effective after
March
28, 1977
(R.
1114,
2016).
A landing procedure known as the two segment approach was
discussed by several witnesses.
While aircraft generally land
using
a three degree slope until touchdown
(R.
3314),
the two
segment approach keeps
the craft at a higher altitude using
a Six
degree slope as
long as possible.
The plane then picks up the
next intercept using three degrees until landing
CR.
3313).
Because the plane itself
is
further from the ground longer,
noise
emissions are reduced by six or seven decibels
(R.
551).
The FAA
decided
not to prescribe the two segment glide slope procedure as
submitted by the USEPA
in its regulatory proposal
(Exh.
145,
41
Fed. Reg.
52388—92, R.
1148).
The FAA found that this procedure
as proposed presented
a safety problem due to an unacceptable
increase
in wake vortex encounters based on current minimum
aircraft separation standards (Id.
at 52391).
In other words,
planes would encounter air turbulence caused by prior planes.
In
order
to allow sufficient time for these wake vortices
to
diminish,
the FAA says the spacing between planes would have
to
be doubled, resulting
in
an increase
in delays and energy
consumption and resulting
in “inefficient use of the national
airspace.”
Id.
Additionally the
FAA
investigated icing
possibilities,
the high sink rate,
effect of tail winds and wind
shear,
a descent rate that may not be met by some aircraft,
69.151

—88—
increased pilot work load and potential airspace and traffic
conflicts
Id.
The FAA concluded that the two segment approach
is
“not consistent with the highest degree of safety
in air commerce
and not
in the public interest.”
(Id.
at 52392).
Benninghoff testified that based on American Airline’s
simulator studies
it was determined that aircraft could handle
a
two segment approach although the upper segment would differ
depending on aircraft type.
He further testified that:
In
fact
all
aircraft
couldn’t
fly
an
upper
segment
of
six
degrees
due
to
weight,
flap
drag,
kinetic
energy,
and
as
I
recall,
from our
simulator
tests
the maximum upper
segment
that
could
be
flown
with
a
Boeing
747 was four degrees,
with
a DC—1O
was
four
and
a
half
degrees, with
a 707
was
five
and
a
half degrees....R.
3250—1, 3321.
The simulator study shows
that while the 6/3 glide slope may
not be feasible, other two segment approaches are, depending upon
the upper
slope
limit.
The airline representative stated that
the two segment approach
is feasible based on an earlier 1971
study
(Exh.
140, NASA),
but that pilots want vertical and lateral
guidance coupled
to the autopilot
(R.
3320—25).
The ATA
maintains that two segment approaches are feasible but that the
FAA has abandoned the idea
(R.
3584).
Preferential Runways
Noise impacts can be reduced by using preferential
runways.
Relief
is gained by using runways near less populated
areas and by switching the use of heavily used runways over
a
certain number
of hours.
FAA approval
is required before using
this procedure
(Exh.
13,
p.
56(d),
R.
2656—9).
FAA policy
proscribes preferential runway use
if there
is more than a
fifteen knot crosswind
at eighty degrees
(R.
3291—3).
Barring
such a wind,
once a controller assigns
a runway,
the pilot still
way refuse
to use a preferential runway for safety
reasons
(Exh.
114,
14 CFR 91.87(g),
R.
2661—66).
If a pilot does not wish to
use
a preferential
runway,
that pilot must wait for
a non—
preferential
runway
(R.
1194).
Other runway options mentioned are the use of over—water
approaches
(R.
1235)
arid the establishment of noise corridors
over tollways for arrivals and departures much like the use of
rivers as noise corridors at Washington National Airport
(Exh.
208 A—D,
R.
4921—3,
5016).
Turning while in flight
is another procedure to avoid noise
sensitive areas.
In fact the FAA has ordered turns at O’Hare
Airport
in Chicago for aircraft departing on runways 27L and 32R
(Exh.
124 Tower Orders,
R.
2884—87).
Testimony showed that
nationally over forty percent of American Airlines aircraft made
noise abatement turns of more than ninety degrees after takeoff
69-152

—89—
(R.
3591—3).
General von Kann testified that such routing costs
more:
You
take
a routing
that,
say,
uses
up
five minutes more
than
a
direct
routing
would
be,
or
two
or
three
minutes.
Now,
you add
fuel,
you add crew
time.
That’s
easy enough
to figure
out.
Then you multiply this by the
thousands
of times you
do
it
and sometimes you do
it and
sometimes
you
don’t
do
it
depending
on
wind
conditions
and other
factors.
I think
it
is obvious on the face
of
it
if you add five niinutes...to
as few as ten percent
of
your
flights,
you
would
come
up
with
a
very
sizable
figure
R.
3153.
One witness said
the use of preferential runways
in Los
Angeles added
ten minutes
to flight time at night,
at
a
calculated cost of
$25 per minute
(R.
3358).
Tax i ing
It was suggested that planes could be towed
to runways
or
use
fewer engines when taxiing.
Such procedures would
reduce
noise
to residents near terminals and runways
(R.
39—40).
An AT4
witness stated that because there are no residences near
the
terminals
at O’Hare, this procedure would not be effective
(R.
3264).
O’Hare area residents disagreed
(R. 4313—18, 4349).
Where
residences are close
to terminals at other
airports, towing
may be
a viable option.
An ATA witness testified that towing would cause problems
for planes which need special starting equipment.
Powerful
tractors with auxiliary electrical
and air start units would be
needed
to
tow the plane.
For those aircraft without onboard
auxiliary power
units,
the tractor would have to start
the
engines of the aircraft
(R.
3264—5).
While testimony suggested
that planes which are taxiing are under federal control
(R.
1951—
3),
it
is not clear whether planes being
towed would
be under
federal control.
Engine Runups
Runup noise includes ground ruriups, which are preflight
engine tests that are part of an aircraft’s regular
maintenance.
Airports can control the location and timing
of
these engine tests and require soundproofing
in maintenance areas
as another noise reduction method.
Aircraft engine maintenance
is frequently conducted at night so that planes are available for
service
in the morning.
The O’Hare noise abatement office claims
that in 1984 it attained 100 percent compliance with its
restriction of nighttime runups
to three locations away from
residences
(Exh.
240).
However,
two citizens at the 1985
hearings complained of runup noise
(S. 62,
239).
Pre—flight
engine runups accounted for bulges
in the noise contours at the
Springfield and Coles County Airports
(R.
1711,
1869).
According
69-153

—90—
to Tiedt,
in 1978 O’Hare averaged three and one—half maintenance
runups per day which were each one to two hours
in length
(R.
6277).
Dr. Zinschlag of the Coles County Airport testified
regarding the importance of pre-flight runups:
The
airport
authority
has
enacted
ordinances...that
forbid
running
up
of
airplanes
in
certain
areas
——
forbid continuing
noise that
is
not
deemed
to
be
absolutely necessary,
for
the safety
of.
the
people
in
the
plane.
We
consider
this
word
paramount
——
safety,
safety.
When
we
fly
an
airplane,
we want to
be safe.
We
want
to
know
that
the equipment
is safe.
We can’t say you can’t
run up
an
airplane
at
the
end
of
a
runway because
it makes
noise before
it
takes off.
The pilot has
to do this
so
he
can check
all
of
his electrical
instruments
to
know what
his engines are
doing
to see ~‘whetherthey
test
out
so
that
he
doesn’t
lose
power
on
a
take
off.
This
is
a
lot
more
impact
than
is
noise
R.
1784.
General von Kann testified that most maintenance
is done at
night and that,
“Sometimes
runups are required following
maintenance
to make sure the engine
is operating normally.”
(R.
3263).
He also said that delaying runups until daytime would
delay morning flights.
Id.
The proprietor of Capital Airport
in Springfield required
one company
to move its aircraft and maintenance facility
to the
opposite end of the airport away from
a subdivision
(R.
1508—
09).
At the same airport the Air National Guard installed a half
million dollar
“hush house” where noise from all of their
maintenance runups
is suppressed
(R.
1510).
When testifying
about ground operations,
Dr. Galloway said that most commercial
operators have test cells and that orientation of aircraft during
tests can help
(R.
5345).
Berms
The use of berms, which are large, narrow ridges of
earth,
could benefit
a large number
of people who live close
to
airports.
Berms are most useful
at reducing noise which
is
generated at ground level.
O’Hare is currently constructing
a
berm that will ultimately be 3,500
feet long and
50 feet high
to
reduce noise
in Berisenville.
Two other berms are also planned at
O’Hare
(Exh.
240).
Construction of a berm at Peoria could
reduce
the noise
to 110 severely impacted homes
to below 65 Ldn
(Exh.
B
at 8—9, Tables 11—2 and 11—3 at 21—2).
Another 2,000 foot berm
at Peoria would protect 22 more homes while
the same size berm at
Decatur would protect 11 homes from noise levels 65 Ldn or over
(Exh.
B at 8—9).
69-154

—91—
Soundproofing
Another noise reduction method
involves the
insulation or
soundproofing of noise impacted homes and schools.
While
insulation does nothing
to reduce the noise
impact at the
receiving property, and therefore would not cause compliance with
any noise standard,
it will reduce the amount of noise coming
into a building.
It may prove useful
in conjunction with
easements and
in demonstrating mitigation.
The authors of
the
EcIS
(Exh.
A,
B,
C, D) found
it
a technically feasible method.
Three schools
in
a 75 Ldn contour near O’Hare have been
soundproofed
(Exh.
240 at
10).
Funding for each school was
eighty
percent federal,
ten percent City of Chicago,
five percent
by the municipality involved and five percent by the local school
district
(Exh.
251,
A,
B,
C;
S.398, S.274).
The result of
soundproofing Washington School was described by the president of
the Board
of Education
in Schiller Park:
I
just mentioned
a
few minutes
ago
to you
that
one
of
the teachers told us
that she saw an airplane
overhead and never heard it, which...was
a compliment
because usually...you just couldn’t teach.
S.
269.
Future school soundproofing may
be
in the offing.
The
federal government has been providing estimates for soundproofing
other severely impacted schools
(S.
273—4).
The City of Chicago
“will extend
its soundproofing program to schools within the 70
Ldn continuous noise contours for 1995....”Exh.
240 at 11.
Additional procedures such as updating building codes
to
require noise insulation
in new buildings, modifications or
expansions could also be useful
(R.
1881,
2096,
2938, 6278—80,
E.
390—6).
Tiec3t testified,
however,
that “none
of
the
communities surrounding O’Hare have building codes which require
soundproofing of new structures.”
(R. 6244).
Insulation and soundproofing, however,
are not panaceas.
One woman testified that:
linsulation
is
an
answer
if
you
can afford
to
air
condition your
home
and
it doesn’t give you
the
privilege
of
listening
to
the birds sing with planes
flying
over,
and so on
S.
105.
Some residents felt that insulation would make them
“prisoners”
in their
homes given the need
to keep doors and
windows closed
(S.
48,61).
There were also comments on the cost
of air conditioning necessitated by closed windows.
One man
estimated that he currently spends 100 dollars per month
on air
conditioning
to help reduce airport related noise
(S.
44).
69-155

—92—
Easements
Besides
insulating buildings,
a proprietor may wish to
purchase a noise easement over the property of
a residence
impacted with noise greater
than 65 Ldn.
For payment of an
agreed—upon fee the homeowner would choose
to experience more
noise while the proprietor would have the right
to subject that
residence to greater
than 65
Ldn.
The easement would be recorded
with the title and would appear
in any competent title search.
An example of
a noise easement
is what the Peoria Airport
Authority terms an “avigation easement,” which
is a combination
of noise
and navigation easements.
The Authority has acquired
approximately 30 to 40 easements over individual homes
(R.
2064—
5).
No cost data have been presented for these easement
purchases.
Differing testimony appears
in the record as
to the relative
cost
of noise easements.
Tiedt stated that the general rule for
easement cost is one third of the residential property value but
that each situation should be evaluated on a case—by—case basis
(R.
6380).
The authors of the EcIS reviewed the literature and
cited four different studies which examined easement costs.
They
settled on the easement costs around Los Angeles
as being
representative of costs in general.
Easement costs range from
2.5
to
17 percent of the property value depending on whether a
residence is in a 65—70, 70—75
or a 75—80 Ldn contour
(Exh.
B at
38).
Upon purchasing
a noise easement,
the proprietor would
be
in
compliance with the noise regulations as
to some Class A
residences.
The Board, however, shares
the belief of the AGO
that easements should be limited
to areas experiencing less then
75 Ldn.
Above this level
a residence becomes essentially
uninhabitable and other options, such
as purchase in
fee simple,
would probably provide more protection to the public, especially
unsespecting potential buyers.
Purchase
Another compliance method is the purchase by the proprietor
of undeveloped land or Class A land from the owner.
Prices paid
would approximate market value, with relocation benefits and
administrative costs added
where applicable,
as where federal
funds are involved.
Use of this approach would change the Class
A use designation of the land.
A consulting engineer testified concerning Capital Airport’s
land acquisition program in Springfield:
lit
became the policy of the airport
to acquire
all properties along
the existing airport’s boundary
and
the future
west belt’s location to eliminate the
possibility
of
residential
development.
It
was
69-156

—93—
believed
in the long—range plan that this land
——
has
been
acquired
and
will
not
be
used
for
aviation
purposes,
such
as
runways
and taxiways.
Long—range
plan
is
to
use
it
for
some
aviation
compatible
business
or
industrial
development.
.....
They
Springfield—Capital
have acquired essentially over
200 acres
in the south portion
of the airport....
There
weren’t sufficient
funds
to acquire
all
of the property at one time, so priority was given to
the property
south
of
the property
sic
——
airport?
because
it
was
still
agricultural
property.
We
wanted
to buy it before it was developed;
so included
in
the
same
program
was
the
acquisition
of
the
residences
immediateiy
adjacent
to
the
northeast
boundary
of
the
airport....
They
have
acquired
the
properties,
and
they have
demolished
the
houses
on
the property.
We
believe this
is just the start
R.
1670—8.
The
Los
Angeles
Airport
purchased
properties
around
its
facility
for
noise
abatement
and passed
the
cost
on
by way
of
landing
fees
(R.
3150—3225).
Greater
Pittsburgh Airport
bought
6,000
acres and demolished
the purchased residences
(R.
6179).
Land
acquisitions
for
noise
abatement
can
be
accomplished
between
a willing buyer
and seller
or by condemnation.
Witnesses
had
mixed emotions
about
having
their
homes bought.
Aside
from
cost considerations,
however,
acquisition
is
the most preferable
solution
for
some airport proprietors.
A consultant for Chicago
said:
In
our
experience
in airport
impact situations,
fee acquisition has tended to be
the most expeditious
way
of
solving
the
problems
and
the
most
final
solution.
Clearly,
there are other
alternatives and
one can debate the
values
of those ad infinitum....
Our
general
experience
has
been
that
the
fee
simple
acquisition
route
is
preferable
to
a
navigation
easement
or
that
sort
of
an
approach,
which
is
an
alternative
to
perhaps
reduce
the
cost.... ER.
6112)
The
impact
of
outright
purchase
of
noise
impacted
homes
depends
largely
on
their
number
and
location.
According
to the
EcIS
there
were
only
2,574
such homes
at downstate airports
in
the
late
1970’s.
About
1,600
were
at
one airport and
1,045
of
those were mobile homes which could probably
be easily relocated
(See Table
3).
The purchase of
those homes and relocation of the
residents would have
a relatively small
impact at most downstate
airports.
69-157

—94—
The
Chicago
airports
are
another
matter.
Mr.
Jeffrey
N.
Thomas,
Vice
President
of
Booz—Allen
Hamilton
Management
Consultants
and
manager
of
operations
of
its
Landrum
&
Brown
unit,
and
Tiedt
of
Landruin
and
Brown
provided
testimony
on
purchase
impacts
for
the
city
using
1979
as
the
base
year
CR.
5886).
Estimates
were
given
for
purchasing
homes,
schools,
hotels,
and
motels
in
the severely
impacted
80
Ldn
contour.
It
was
noted
that
federal
funds
may
be
used
for
acquiring
noise
impacted land
(R.
6250).
At O’Hare
2,320
homes
were within the
80 Ldn contour.
The
purchase
costs
were
estimated
at
119.6
million
dollars
with
relocation
and
demolition
costs
adding
about
83
million
dollars.
Total
costs
for
Class
A
acquisition were estimated
at
295.14 million dollars (Group Exh.
223,
“Exh.
19”, R. 5928—30).
This
acquisition
would
cause
certain
economic
and
social
disruptions
in
six
communities
surrounding
O’Hare.
Wood
Dale
would
lose
30.7
percent
of
its population ~hile
Rosemont would
lose
0.2
percent.
The
estimated
reduced
tax
extension
as
a
percent
of
total
revenues
ranged
from
9.0
to
0.1
percent
for
communities,
7.9
to
0.1
percent
for
high
school
districts,
and
14.9
to
0.2
percent
for
grade
school
districts
depending
upon
their
location
(Group.
Exh.
223,
“Exh.
20—23”,
R.
5939—5940).
Thomas pointed out that the tax base would be expected
to recover
as
industrial
development
occurred
on
former
Class
A
lands
(R.
5940).
If
the 65 Ldn
contour
is
used
as
an acquisition guide,
the
impact
would
be
much
greater.
Portions
of
approximately
45
communities
around O’Hare
and
20
around
Midway
are within
these
contours
(R.
6283—85).
It
is estimated
that up
to 86,400 homes
are
in the O’Hare contour
(Exh.
240) and Midway has between 6,000
and
36,000
depending
upon
its
level
of
activity
(See Table
4).
Purchasing
homes
with relocation
costs
in the
65
Ldn contour
at
Midway
was
estimated
at
over
3.2
billion
dollars
(Group.
Exh.
223,
“Exh.
54”,
R.
5994—95).
~j~ghttimeCurfew and Reduced Operations
Reducing
noise
by
cutting
back
flights
or
imposing
a
nighttime
curfew
received
an
overwhelmingly
negative
reaction
from proprietors, airlines and industry.
Because O’Hare would be
the most significantly impacted by cutting back operations,
this
discussion
will
focus
primarily
on
that
airport
while
other
airports will
be discussed
in the economic
impact
section.
The
industries
negative attitude
was adequately
summed
up
by Thomas
while testifying
for the City of Chicago:
In
terms
of
repercussions
of
flight
reductions
on
the national aviation system and air
service,
the
impacts
are
for
all
intents
and
purposes
incomprehensible given
the central role of O’Hare as
69.158

—95—
the
primary connecting
facility
in the northern
tier
of
the national airport system....
0
‘Hare
is
absolutely
crucial
in
its
role
as
a
connecting
facility.
The specific adjustments which
would
have
to
be made
by each airline
serving O’Hare
necessitated
by
reducing
flights
are
impossible
to
predict.
The
economies
of
operation
obtained
by
loading
partially
filled
airplanes
with
connecting
passengers
would,
to
a
large
degree,
be
lost.
Certain
markets
would
certainly
suffer
cutbacks
in
service.
Massive
shifts
of
activity
to
other
large
midwest
airports,
such as
St.
Louis
or
Kansas City,
would quickly
increase congestion at these facilities
producing unacceptable system congestion.
Moreover,
shifting
the
noise
problem
to
other
localities
would
certainly
occur
if
connecting
activity
were
transferred
to
other
airports,
simply
does
not
solve
the
aviation
noise
issue.
More
importantly
to
the
State,
an
immediate
decline
in
employment,
payroll
and
expenditure
levels
would
be
experienced
ER.
5920—21
Due to the nature of
the Ldn formula,
a rather large
decrease
in operations
is necessary
to achieve
a small drop in
measured noise.
Studholme provided a general assessment of the
amount of operations reduction required
to reach
a specified
reduction in noise:
To obtain
a one—decibel decrease, you would need
a
21—percent
reduction.
To
obtain
a
two—decibel
decrease, you would need
a 37—percent
reduction.
To
obtain
a
three—decibel
decrease,
you
would
need
a
fifty—percent
reduction.
To
obtain
a
four—decibel
decrease,
you
would
need
a
sixty—percent
reduction.
To
obtain
a
five—decibel decrease,
you would
need
a
sixty—eight—percent
reduction.
And
if
you
wanted
to
obtain
a
ten—decibel
reduction,
you would
need
a ninety—percent reduction
in the operations at the facility.
This assumes
that
everything else remains constant;
there are the same
number
of
aircraft
flying
during
the
night,
same
during the day,
same type of aircraft, same
mix, and
that things don’t change over the period of
time when
the reduction is taking place
S.
290—913.
Curfews on night operations are often discussed because they
create more disturbance.
Also in the Ldn formula,
the
elimination of one night flight
is equal
to ten day flights.
Mr. Ian Bamber, Director
of Schedule Planning and Analysis
for United Airlines, provided detailed information on the
69-159

—96—
importance
of maintaining O’Hare’s current operations.
In his
opening statement,
he pointed out that a complete nighttime
curfew and eliminating 32 percent of day flights would only
reduce
the noise
level
by five decibels.
Discussing the impact
of such actions, Bamber called O’Hare “the most important single
airport facility
in the world”
(R.
3988)
and that
in 1979,
it
provided single plane sevice to over 200 U.S. cities and 33
foreign cities.
It is also a major aircraft maintenance center
(R.
3987—99).
In
a similar vein, Thomas testified that O’Hare
is the focal
point of the northern tier of the nation’s air transportation
system.
Passengers connect there
to meet flights
to destination
cities.
O’Hare had about 18,000 interline (arrive and depart on
same airline) city—pair connections
in 1971 and 7,000
intraline
city—pair combinations.
The largest of these contributed only
one percent of
the total
intraline connections
(R.
5945—46).
In
commenting on this, Bamber
said:
Because
of
the complex interrelationship of all
of
those
factors,
it
is impossible
to cancel
flights
at
any
one
station,
particularly
an
important
one
like
O’Hare
without
disrupting
or
completely
eliminating
flight
schedules
between
other
pairs
of
points which precede
and follow
the flight cancelled
at
the
affected
station.
Any airline
cancelled
at
O’Hare
would
definitely
affect
airline
service
literally all
over
the couhtry by every airline
that
serves
the O’Hare Airport.
Taking
a
flight
out from the middle of
a flight
sequence,
especially
to major
maintenance point
like
O’Hare,
is
like
taking
the
bottom
card
away
from
a
house of cards
ER.
3999)
Bamber provided several examples of how
reductions or
a
night curfew could impact flights.
He used Boise
as
an example
of the importance of connecting flights:
The
Chicago—Boise
market
is
a
very
good
example.
From
Chicago
to
Boise,
Idaho,
the
local
market
is
only
35
passengers
a
day.
That
is
not
economical
to provide nonstop airline service
in that
market
for
35
passengers
daily,
even
if
they
all
wanted to go at one time of the day.
However,
there
are
two
daily
flights
nonstop
between Chicago and
Boise;
and the
reason
there are,
is because
we
are
using
connecting
traffic which
is
wade
possible
by
bringing
in
these
large
connecting
banks
from
the
East
into
Chicago
to
connect
with
Boise.
69-160

—97—
Combining
it with
the
local market, we are able
to
generate
a
load
to
support
two nonstop
flights.
If
there were
rio
connections
from Chicago
to
Boise,
we could not support a connecting flight
to Boise
R.
4061—62)
He used a Honolulu to Chicago flight
to demonstrate one
impact of
a curfew on flights between 10:00 p.m. and 7:00
a.in.:
United’s
Flight
114
is
a
747
which
originates
its
day
at
9:00
a.m.
in
Honolulu,
operates
through
Los Angeles
at
5:00 o’clock
to Denver,
and continues
on
from
Denver
and
arrives
in
Chicago
at
1:30
a.m.
the following morning.
Under
a nighttime curfew at O’Hare, we will have
to cancel the Denver—Chicago segment.
It is the last
departure from Denver
to Chicago.
It has night coach
fares.
It
is
very popular
for
the
passengers;
and
since
the
Denver—Chicago
market
has
no
cargo
line
service,
it
provides
a
very,
very
heavy, cargo
and
mail
flight
into
Chicago.
Therefore,
Flight
114
would have
to be terminated in Denver.
There will be
no
daylight
service
available
from
Honolulu
to
Chicago.
Los
Angeles
would
lose
its
late
evening
6:00
p.m.
departure
for
Chicago,
and
Denver
would
lose its nonstop flight.
But
not only
that,
when the
airplane gets into
Chicago
it departs again at 8:20 on Flight
193 and
it
retraces
its
steps:
Chicago—Denver—Los
Angeles—
Honolulu.
Since
the
airplane
and
crew are
in
Denver,
we
would
have
to
cancel
the flight
Chicago—Denver.
So
again,
Chicago
will
lose
valuable
service
in
the
morning.
It will
be an outright cancellation.
There
will be no value to retiining it because we don’t have
an
airplane
and
crew
of
that
type
available.
Therefore,
O’Hare
would
lose
the morning
service
to
Denver and Los Angeles, which is
a very popular one.
Again,
going
back
to
Flight
114,
if
you wanted
Flight 114
to operate into Chicago before 10:00 p.m.,
it would
have
to
originate
at Honolulu at
5:30 a.m.
in
the
morning.
That will
be
a very unpopular
time
in
a
market
like
Honolulu—Los
Angeles
and
an
imposition on passengers destined for Los Angeles and
Denver.
The
airplane
also
provides
a
prime
after—
business departure
from Los Angeles
to Denver.
That
would
be moved up
to around 2:00 p.m.
or 2:30, which
69-161

—98—
is very early
if you
finish your business day and get
out
to the airport.
The
fact
that
it
is
very
heavy
for
mail
and
cargo,
a
night
coach
flight
from Denver
to
Chicago
would
be lost because
the flight would have to depart
Denver
too
early
to
be
able
to pick
up
the mail
and
cargo
from
the
night
before,
and
night
coach
fares
will not apply at that early time
R.
4021—24.
Bamber discussed other problems related to
a curfew.
Planes
fly into Chicago for major maintenance.
Over half arrive after
10:00 p.m.
and leave between 6:00 and 7:00 a.m.
Changing this
would have
a ripple effect throughout the schedule
(R.
4008,
4110).
Over 6,900 people
who
use night flights each day
would
be
inconvenienced
(R. 4128).
A curfew would also disrupt
cargoflights since
60 percent of cargo arrives at night
(R.
4010).
The U.S. Mail service is highly dependent on night
flights
(R.
4015,
5957).
Both Bainber and General von
Karin agreed
that night flights could not be shifted
to daytime because of
existing congestion
(R.
3171, 4026).
Dr. Richard R. Shaw,
an Assistant Director General—Technical
for the International Air Transport Association, testified that
O’Hare ranks fourth
in the nation
in international passengers
(R.
4387).
It would be difficult
to use alternate airports for these
passengers since they must enteT
the country through a port of
entry
(R. 4408).
He also pointed out that most international
agreements provide
for no restrictions on airline service
(R.
4427).
Some cities do impose full or partial curfews.
These
include Kansas City, Houston,
Los Angeles, Washington National,
as well
as Geneva,
Sidney, Tokyo—Narita and Hong Kong
(R.
4028,
4422).
The impact of curfews depend on such factors as their
location, numbers of connecting flights,
and availability of
alternate airports.
Bamber pointed out that curfews
at
Washington and San Diego do little damage
(R.
4073).
Reducing airport operations would also have important
secondary effects on the economy of the entire Chicago
metropolitan area.
Approximately 27,300 people work at O’Hare or
its off—site locations.
The payroll
in 1979 was $536 million.
Indirect employment such as hotel/motel,
air cargo firms and
freight forwarders brought the total employees
to 75,652 with an
annual payroll of $753.71 million.
When induced employment was
added
the number
reached approximately 124,403 people with
a
payroll of $1.46 billion
(R.
5916).
The total economic benefit
of the airport including payroll and direct and indirect
expenditures was estimated at $5.68 billion.
The economic impact
study conducted
in conjunction with the O’Hare Master Plan found
that in 1976 O’Hare ranked as the seventh leading employer
in the
Chicago Metropolitan Area and
(combined with Midway) represented
approximately 0.7 percent of the metropolitan area employment and
69-162

—99—
5.3 percent of
the gross metropolitan product
in 1977
(R.
5918).
Much of his analysis related
to how the compliance
options would reduce overall economic activity.
The first scenario involved reducing O’Hare operations to
a
level that would shrink the noise contours
(80 Ldn) such that
they would not reach Class A land
(R.
5919).
Thomas listed
the
cutbacks necessary
to meet this standard:
A total
reduction of 43 percent of day and
all
nighttime operations would have been required
in 1979
in order
to comply with the 80 Ldn noise
level,
that
is,
so that no Class A land would be affected....
To reduce exposures
of Class A land
to levels of
80
Ldn
or
higher,
the
following
cutbacks were made:
All military
operations
were deleted;
all
air
cargo
flights were
deleted;
commuter,
air
taxi and general
aviation
traffic
was
reduced
by
45
percent;
international
scheduled
traffic
was
reduced
by
46
percent;
domestic
scheduled
traffic,
as
I
have
already discussed,
was reduced by 46 percent.
I
think
the
implications
of
these
cutbacks are
awesome,
requiring
the elimination
of
1,091
flights
each day
R.
5947—48.
This scenario would result
in an annual loss of $2.02
billion dollars annually.
In addition
to this,
flight fees to
remaining aircraft operations would probably be increased to
cover losses
in airport revenue due
to the reductions.
This
would put O’Hare at
a disadvantage and might
lead to further
reductions
CR.
5924).
According
to the marketing director for
the Greater O’Hare Association of Commerce and Industry, a major
reduction at O’Hare would also severely impact the surrounding
communities
as
“17 out of every 100 jobs”
in the area were
directly tied
to O’Hare
(R.
5252).
The second scenario involved purchasing impacted Class A
lands and evaluating the fiscal and social costs of this action
on those communities affected by such
a policy.
The social
impacts
of this option were discussed
in the section on land
purchase.
In economic terms,
the economic cost of this scenario
to O’Hare was given as
295 million dollars
in
a one time
expenditure.
(Gr.
Exh.
223,
“exhibit 19”,
R.
5928—30).
The third scenario eliminated night flights and purchased
the remaining impacted Class A properties.
This reduction would
lead to
a loss of 400 million dollars annually and require
property acquisition costs
of approximately 40 million dollars
(Group Exh.
223,
“Exhs.
27,
29”,
R.
5949—51).
At Midway, meeting the
65 Ldn standard would require
reducing operations
to 20 per day, meaning a maximum of
10
69.163

—100—
flights
(R.
6209).
Purchasing 36,600 homes under an un-
restricted activity option would cost over 1.5 billion dollars
(R.
5968).
Thomas testified under questioning that the Landrum and
Brown analysis did not consider obtaining
a variance
to avoid the
need to reduce service or purchase land.
It also did not take
into consideration other alternatives or combinations of
alternatives for reducing noise impacts
CR.
6125).
It did not
attempt
to put
a value on the impact of noise
on surrounding
residents
CR.
6109).
Land Use and Zoning
Testimony on the role that land use planning can play in
preventing additional noise problems around airports has been
discussed
in prior
sections of this Opinion.
It
is not necessary
to repeat
those observations here.
A 1983 DENR report titled A Demonstration of Airport Noise
Impact Mitigation
(Exh.
239) reviewed options for addressing land
use issues.
Two attorneys,
Roger W. Findley, Professor of Law at
the University of
Illinois and Daniel King discussed the
law in
this area and potential problems that local airport noise zoning
ordinances may encounter.
They concluded:
Zoning
for
noise—compatible
development
around
airports
has
not
been
addressed
directly
by
the
Illinois
courts
or
the
Illinois
General
Assembly.
However,
it
seems probable
that
local governments
in
Illinois
may
prohibit
noise—sensitive
uses
in
the
area
near
airports,
through
the
exercise
of
either
general
statutory
zoning
authority
or
home
rule
powers.
Such
a
local
prohibition
should
be
vulnerable
to
attack
only
if
there
is
no
reasonable
basis
in
fact
for
the
determination
that
the
airport’s
present
or
future
noise
levels
would
be
incompatible
with
the
physical
or
mental
health
of
residential
users
of
the affected
land,
or
if
there
is
no
profitable,
nonresidential
use
for
such
land....However,
in
order
to
ensure
that
the zoning
is
able
to withstand challenge,
the
local government
must
be
able
to
demonstrate
that
the
exclusion
of
residential uses
is consistent with
the public well-
being
and
the
general
use
of
the
district.
The
exclusion of residential
uses
is
likely
to
be upheld
where
land
use
prior
to
adoption
of
the
noise—
compatibility
ordinance was nonresidential,
that
is,
agricultural,
industrial,
or
commercial
Id.
147,
152
Exhibit 239, Appendix H contains suggested language for
amendments
to the Airport Zoning Act.
Ill.
Rev. Stat.
1985,
ch.
69-164

—101-
15
1/2
,
par. 48.1 et
seq.
The amendments were recommended by the
Illinois Public Airports Association and provide that:
1.
The Illinois Pollution Control Board
(IPCB) would
establish the noise standards necessary to protect the
environment, comfort and general welfare of the public
from airport noise
in noise—sensitive areas.
2.
No person could construct any new structure or make new
use of any existing structure in any area where the
noise levels have been established by the IPCB unless
it
is demonstrated
to the Illinois Environmental Protection
Agency
in
a permit proceeding that the interior noise
levels would
be below
the levels established by the
IPCB.
3.
Every political subdivision with
a noise
zone located
wholly or partially within its jurisdiction would have
to adopt airport zoning regulations !or that part of
such noise zone consistent with items
1 and
2 above.
4.
Where
a noise zone exists
in connection with
a publicly
owned airport,
the Department of Transportation would,
on request of the political subdivision
in which the
zone
is located,
adopt and enforce airport zoning
regulations consistent with
items
1 and
2 above
Id.
58
Findley and King also considered
the possibility
of “truth
in sales” provisions
to require notification to buyers of
potential noise impacts.
They concluded:
There appears
to be authority
to support
a noise
disclosure
ordinance
in
home
rule
communities
that
would
extend
to
all
sales and
leases
of
residential
property.
Such
an
ordinance could
be enforced by
a
penalty
provision,
applied
to
the
agents
of
a
property owner as well as
to the owner himself.
The home rule ordinance, however, has two severe
shortcomings:
it
could
not be
applied
to property
outside the home rule unit’s boundaries,
and
it could
not
be
enacted
by
a non—home rule government.
There
is
no
apparent
authority
by
which
a
non-home
rule
government
could
adopt
a
general
noise
disclosure
requirement.
The
use
of
building
codes
and
zoning
ordinances,
as
well
as
reliance on
state
regulation
of
realtors,
seems
to
offer
no
practical
means
of
achieving effective disclosure of local airport noise
conditions.
Local
control
over
new
subdivision
development,
however,
may
provide
some
partial
satisfaction
of
the
community’s
interest
in
having
noise
conditions
fully
disclosed
to
prospective
residents
Id.,
132.
69.165

—102—
Alternate Airports
Shifting traffic from crowded, noisy airports was also
discussed as
a possible alternative.
Such shifts are difficult
for most passenger service,
but are taking place on a small
scale
for certain passenger and freight operations.
Rockford,
for
example, has been obtaining freight and private jet service since
it
is relatively convenient
to the Chicago metropolitan market by
surface transportation
(S.
417—19).
General von Kann commented
on the problems major shifts to alternate airports would cause:
Now,
shifting
aircraft
to
neighboring
airports
is also one of the alternatives
to be considered.
In
the
case
of
O’Hare
a
very
large
number
of
flights
would
have
to
be
shifted
to
produce
a
significant
noise reduction.
Such shifting would mean
(A) moving
flights
to Midway,
which
is unattractive because the
airport
is virtually surrounded with Class A land and
only
limited
large
aircraft
frequency
could
be
tolerated
before
it
too
would
violate
the
regulations,...(B)
A
major
transfer
of
flight
to
airports
serving
other
regional
cities
not
affected
by
these
regulations
——
by
its
regulation,
for
example,
South
Bend,
Fort
Wayne,
Janesville,
Milwaukee,
or
St. Louis.
Now,
this would represent
a
significant loss
of
airline
service
to
Chicago
and
to
Illinois
and
an
irreparable
injury
to
the
economy
of
the
city
and
state
and
a
shifting
of
the
flights
would
seriously
impair
the passenger,
freight,
and mail traffic that
must utilize O’Hare as
a connecting point.
Moreover,
some
of
these
other
airports are
not
operationally
capable
of
accommodating
all
of
the
aircraft types utilizing O’Hare now and
in the future
fR.
3065—66, July 27,
1978.
Bamber also commented on the problems associated with
a
major shift
to alternate airports:
It
will
be
literally
impossible
to reconstruct
any meaningful part
of the O’Hare connecting complex
at
another
airport.
The
connecting
traffic
that
is
aboard the flights,
which
would
be unable to connect
at
that point,
would most likely have
to use surface
transportation
back
to
O’Hare
to
continue
their
journey beyond.
Most
of
the
service
at
Midway
is
new
service,
rather
than
existing
flights
diverted
from
O’Hare.
Based
on
our
experience
of
operating
at
Midway
from
1970
to
1973, Midway does not have the complex or the
69.166

—103—
airport
capability
to
serve
the
majority
of
connecting
passengers
that
right
now
are
going
through O’Hare
ER.
4072.
ECONOMIC IMPACT STUDY
In regulatory proceedings, the Board
is
required to consider
the technical feasibility and economic reasonableness of the
proposed regulation.
Ill.
Rev. Stat 1985,
ch.
ill
1/2
,
par.
1027(a).
Celotex Corp.
v. Pollution Control Board,
94
Ill.2d.
107,
121—124,
445 N.E.2d 752
(1983).
The Board must make
a
finding as
to technical feasibility and economic reasonableness
pursuant
to Section 27(b)
of
the Act.
Citizens Utilities Company
v. Pollution Control Board, et al., No.’s 84—0412,
83—0498
consol.
(3rd Dist.
1985).
The Board will examine the effect of
the proposed regulation
first on the downstate
(outside Chicago)
airports and secondly on the O’Hare and Midway airports.
The Department of Energy and Natural Resources
(DENR)
formerly (IINR)
submitted
a four volume economic impact study
(EcIS) which considers
the different alternatives available
to
meet
the phased
in noise standards,
the respective costs,
and the
relationship
of costs
to benefits of the proposed regulation
(Volumes
I,
II,
III and IV are Exhibits A,
B,
C, and D
respectively).
Prior to development of the economic impact study,
24 public
airports including O’Hare and Midway were expected
to be in
violation of the proposed 65 Ldn noise standard
(Vol.
I, Table
2—
1 at 11).
After study,
the EcIS consultants found that 17
airports
(14
in Vol.
I, Table 1—2 plus O’Hare,
Midway,
and
Lansing) would violate the
65 Ldn noise standard
(Vol.
I at
1,
Table
1—2 at
4, at 119).
At the time of the EcIS there was one
dwelling unit off the end of runway 27 at Lansing,
a non—jet
airport, which would be subject to noise
in excess of
65 Ldn.
(Vol.
I
at 119).
It apears
the authors also dropped
consideration of East Aiton—Civic Memorial Airport under
the
three levels
of noise mitigation methods
(Vol.
I at
82, Vol.
II
at
xi).
The analysis
of airports will
be separated into
consideration of downstate and Chicago airports, beginning with
the
12 downstate airports which the EcIS assumed would violate
a
65 Ldn standard.
For the purpose of determining
the economic
impact of the regulation,
the consultants studied
three levels of
action airports could take
to reduce their noise impact
(Vol.
I
at 6).
Methods least disruptive of service were considered first
in the first level.
Level two results
in changes in time or
type
of service while level three consists
of service reductions.
The
levels were described
as follows:
69-167

—104—
Level
1:
operational changes such as departure headings,
noise abatement turns, preferential runways,
and
barriers and berms
(where needed);
Level
2:
elimination
or reduction of nighttime operations of
whole classes of aircraft but their addition to
daytime operations
to escape
10 dB nighttime
penalty;
Level
3:
total elimination, both night and day,
of some
types
of jet aircraft operations.
These groups of methods do not represent the only noise
reduction actions which can be taken.
They are illustrative of
one way of meeting the proposed 65 Ldn standard which was
convenient for economic analysis.
They do not consider variances
or other
relief from the standard.
Every public airport
proprietor will have
to determine what method or combination
of
methods would lead that airport into compliance with a
65 Ldn
standard.
The authors of
the EcIS chose
a certain combination
of
methods whose
costs
are presented below.
It
is
important to
remember
that for purposes
of the EcIS the authors predicted that
the noise levels would not grow significantly from 1981 through
the year
2000 but would increase only by one
to two decibels
(Vol.
I at 8—9).
Downstate Airpprts
At
the
12 downstate airports 2,575 dwellings were located
within the 65 Ldn contours.
Of these,
1,045 were mobile homes.
Column A of Table
3 gives the number
of residences near each
airport which were exposed to 65 Ldn or more
(vol.
II,
Table 11—1
at 5,6).
Of the impacted homes four
(0.2 percent) were subjected
to over
75 Ldn, one hundred forty
(5.4 percent)
to 70—75 Ldn, and
2,431
(94.4 percent)
subjected to 65—70 Ldn.
Breaking down the
figures
as
to location,
62 percent were located at Moline—Quad
Cities and
24 percent at Peoria, accounting
for 86 percent of the
homes.
The remaining 14 percent were scattered among the
remaining airports.
Three of
these airports have from 34 to 54
affected dwellings while six have 0.25 or fewer such dwellings.
Id.
From these figures,
the authors of the EcIS concluded
“thus
the downstate airport problem is essentially one of
reducing noise levels by relatively modest amounts for the great
bulk of the affected properties.”
(Vol.
II
at 7).
In reducing noise levels at the downstate airports, level
one methods would only be applicable at four
(Decatur, Quad—City,
Peoria,
and Capital).
These would reduce
the number of Class A
dwelling units subjected to 65 Ldn or more by seventy—five
percent
(Vol.
II
at 8).
Column B of Table
3
gives
the number
of
residences which will be exposed
at 65 Ldn or more after
level
one is
implemented.
69-168

—105—
TABLE
3
NUMBER OF NOISE IMPACTED HOMES AND PERCENT REDUCTION IN JET
OPERATIONS AT DOWNSTATE AIRPORTS FO~VARIOUS LEVELS OF NOISE
ABATEMENT
Airport
A
B
C
D
E
Champaign—Willard
17
17
100
9
50
Danville—Vermillion
10
10
87
0
0
Decatur Municipal
148
44
74
0
0
Galesburg
3
3
27
0
0
Moline—Quad City
15982
228
100
117
80
Mt. Vernon
40
40
100
10
37
Peoria
621
144
100
24
37
Quincy
1
1
42
0
0
Rockford
25
25
100
16
80
Springfield—Capital
36
17
100
4
37
Waukegan
54
393
100
1
20
West Chicago DuPage Co.
21
24
100
9
37
TOTAL
2574
592~
NA
190
NA
A:
Number of residences subject
to noise levels
in excess of 65
Ldn.
B:
Number
of
residences exposed
to
at least 65 Ldn after
implementation of level one noise reduction measures.
C:
Percentage of jet operations which must be rescheduled
to
daytime under level two night curfew measures.
D:
Number
of residences exposed
to at least 65 Ldn after
implementation of levels one and two.
E:
Percentage of
jet operations that must be eliminated
(level
three)
to comply with 65 Ldn after levels one and two are
implemented.
SOURCE:
Data from tables
11—1 and 11—22 from Vol.
II.
1 This table assumes that proprietor does not choose to purchase
noise easements, buy outright or insulate homes and does not
seek
a variance
or other relief from the regulation.
2lncludes 1,045 mobile homes.
3Is given as
54 on other tables
in EcIS.
41s given as 607
in other
tables,
the Board will
use 607.
69-169

—106—
Level one methods include the use of changes
in departure
headings amounting
to five
to ten degrees at Moline—Quad City,
Decatur and Springfield
(Vol.
II at 8—9).
The costs were
predicted to be
zero.
Another method involves the construction
of
a 2,800 foot berm along the southeast sideline of
runway 22 at
Peoria.
The berm would reduce noise levels to 110
of 621 homes
at
a cost
of $313,600
(Id. at 9).
The use of additional preferential runways was considered
useful only at Peoria and Decatur
(they are already used at
Rockford and to
a certain extent Decatur)
(Vol.
II
at 9).
The
authors calculated the annual costs associated with possible taxi
delays and costs arising from air delays
(increased flying time),
components of which included aircraft operating and maintenance
costs and passenger delay costs
(Vol.
II
at
9).
At Peoria,
a
change
in the percentages of flights allocated
to different
runways would result
in
a reduction of taxi time.
This reduction
would save $13,768
in ground operating costs
for general aviation
jets and $5,937
in passenger time for
a savings of $19,705
in
ground taxi costs.
(Vol.
II at 19).
In theair
the aircraft
would have to turn after takeoff which would result
in added
flight costs of
$20,186 and added delay for the passenger,
costing the passenger $6,863
of his/her own time.
Id.
The total
of $27,049
is the cost during flight due
to preferential runway
use.
Taken together,
the ground savings of $19,705 and the added
flight costs of $27,049 yield
a net cost
to general aviation jets
at Peoria of $7,344
(Vol.
II at
19).
For commercial jets,
the
savings of
$104,483
(less ground time)
and the added flight costs
of $143,824 yield a
net cost
to commercial jets at Peoria of
$39,341 due
to preferential runway use
(Vol.
II at 19—20).
The use
of preferential runways
at Decatur would similarly
reduce
the taxi time of aircraft
(Vol.
II
at
10).
For
general
aviation jets this would result
in savings on the ground of
$17,992 but added flight costs of $6,617
for
a net savings of
$11,375
(Vol.
II at 15).
Ground savings of $60,324 but added
flight costs
of $22,248 yield
a net savings of $38,076
for
commercial jets
(DC—9) at Decatur
(Id. at 17).
Several methods of reducing noise impact were not
specifically included
in the level one analysis even though they
are less drastic than levels two and three.
They include the
purchase of noise easements over homes, purchase
in fee simple
and insulation for soundproofing.
The EcIS considered
the cost
of implementing
these methods on the 607 homes which would still
be impacted after the implementation of level one noise reduction
methods.
Noise easement costs vary
as percentages
of property values:
2.5 percent for property
in a 65—70 Ldn contour,
9 percent in a
70—75 Ldn contour,
and 17 percent
in a 75—80 Ldn contour
(Vol.
II
at 38).
Total cost for easement purchases for the remaining 607
homes
at the downstate airports would be
$824,950.
If easements
were required only for
70 Ldn or greater contours,
then the total
69-170

—107—
easement cost
for these airports would drop
to approximately
$318,000 based on the number of homes
in existence at the time of
the EcIS
(Vol.
II
at
38).
Easements plus
level one reductions
would cost about $1.14 million.
Property acquisition also includes the purchase by the
proprietor of undeveloped
or residential property.
Prices paid
by proprietors would approximate market value, with relocation
benefits and administrative costs added.
The costs of
undeveloped land is substantially less than land with
residences.
The EcIS authors looked only at property with
completed residences.
The
total costs of property acquisition
(607 homes)
after level one reductions was estimated at
$29,340,567.
This cost calculation does not take into account any noise—
compatible land reuse.
Reallocation and resale
of these
lands
for noise—compatible uses such as for farming or
industrial
development can significantly diminish the total cost.
It may
also be possible
to convert homes
to office space.
Once
acquired, the property land use designation would be
longer be
Class
A,
thereby complying with
the proposed regulation.
The remaining impacted homes could also be insulated
to
reduce
indoor noise levels.
The total cost of such insulation
was estimated at $2,001,600
(Vol.
II, Table 11—8 at 32).
This
approach, however, would do nothing
to
reduce outdoor noise.
Referring
to Table 11—8
(Vol.
II at 32),
the authors found
that over 50 percent
of insulation costs at downstate airports
would be
for homes requiring
5 decibels or less of quieting, with
the
remaining mostly
in the 5—10 decibel reduction range.
The
average cost per dwelling was estimated at $3,300.
Id.
The
authors mention that
a substantial portion of
the insulation cost
can be recovered, presumably through energy savings.
The authors note that the estimated insulation cost may
be
low since
it is based on decreasing
the noise
in one decibel
increments.
In any major
insulation program,
the cost may differ
per decibel depending on the design, structure and materials of
each house.
The authors hypothesize that
if one,
two or three
decibel reductions by insulation are not perceived as helping by
the homeowner, there may have
to
be
a minimum insulation
requirement of
a five decibel reduction
(Vol.
II at 33).
Another alternative studied was a purchase guarantee program
whereby the proprietor guarantees the fair market value of the
property.
If
a homeowner could not obtain such value,
the
proprietor would pay the fair market value or pay the homeowner
the difference between fair market value and the best market
offer
(Vol.
II at 456).
No costs were presented.
Use of this
technique alone would not reduce the amount of noise
to the Class
A receiving property.
69-171

—108—
If level one reductions and the alternative procedures
outlined above do not bring
an airport
into compliance and a
variance or other
relief
is not sought,
then the proprietor
may
have to consider level
two reductions.
These would include
rescheduling nighttime jet operations
to daytime operations
to
avoid the ten decibel nighttime penalty.
Level two reductions
could be used in conjunction with the other alternatives
mentioned above.
Columns C and D, respectively,
of Table
3 give
the percentages of nighttime jet operations that would have to be
rescheduled
to implement level two and
the remaining residences
that would still
be exposed
to more than 65 Ldn.*
A partial
reduction of night flights
at four of the twelve
airports would bring them into compliance while
100 percent night
curfews at
the remaining eight would still not bring them into
compliance.
Two of the eight would have four or fewer
homes
still
impacted by over
65 Ldn,
and three would have nine or ten
homes so situated
(Vol.
II at 49).
Thus, the eight remaining
downstate airports
(listed
in Vol.
II, Table 11—12, Vol.
II at
55) would have
to implement level
three daytime operational
cutbacks
as well
to come into compliance unless alternative
measures such as easement, property purchase or variance were
instituted.
For example,
if Champaign—Willard Airport bought an
easement
over the two remaining dwellings or purchased them,
the
reduction in daytime operations may not be needed.
The same
is
true of
the single dwelling at Waukegan which otherwise would
command
a
20 percent reduction to achieve compliance,
the
four
dwellings
at Springfield which would command a
37 percent cut in
daytime operations,
and
so on.
The percentage of
jet flights
that would need
to be eliminated under
level
three reductions to
achieve compliance with
a
65 Ldn standard
is given
in column E of
Table
3.
The EcIS did not place an absolute dollar cost on the level
two and three methods because “unfortunately there
is no simple
way of measuring
these costs and attaching
to them a dollar
figure which could
later
be added
to the other costs of noise
abatement.”
(Vol.
II
at 50).
The substantial problems to
travelers and business that would result from curfews and
reductions
in service are discussed elsewhere
in this Opinion and
will not be repeated here.
Eliminating
flights
is
a mitigation measure
of last
resort.
Airports generally attract new
facilities,
create new
investments and jobs, and increase the demand for local goods and
services,
thereby increasing local revenues.
Impacts on an
Appendix B
to EcIS Volume
I contains day and night flight takeoff
data which also incorporates computerized data
in Tables B—2
(Decatur), B—3
(Peoria), B—4
(Moline—Quad City)
and B—S
(Rockford)
(Vol.
•I at 150—7).
Table Il—il
(Vol.
II at 49)
tabulates the effects of night curfews
at the downstate airports.
69-172

—109—
airport affect
the area economy.
Reduced flight availability and
fewer connecting flights can reduce
the attractiveness of the
area to new businesses and disrupt air cargo schedules.
Some
of
this impact can be mitigated by substituting equivalent propeller
service for eliminated jet service
(Vol.
II
at 60—1).
On this
point the authors commented,
“that at some downstate airports jet
service recently has decreased
as a result of airline
deregulation by the C.A.B.,
and that there has been an increase
in the number
of commuter airline flights by propeller aircraft.”
(Vol.
II
at
56).
The EcIS authors attempted
to place a dollar value on the
benefit
to be achieved by noise
reduction.
They used the
regression and legal methods.
The regression method
is based on
estimating
the charge
in property value associated
with
noise
levels.
The legal method
is based on inverse condemnation
recoveries
as
a measure of property value.
Studies
in a number
of cities determined that the percentage
depreciation
(appreciation)
in property value per decibel
increase
(decrease)
in
the noise
level varied from
0.29
in
Cleveland to 1.10 in Washington, D.C.
The mean value was 0.58
percent.
The authors used the mean value for their estimates by
the regression method.
(Vol.
II at 90—91).
Using the inverse
condemnation method,
the report concluded that reducing noise 1—5
dB (from 70
to 65 Ldn) benefitted the property 2.5 percent,
from
6—10 dB (from 75 to 65 Ldn)
9.0 percent and from 11—15 dB
(from
80
to 65
Ldn)
17 percent
(Vol.
II at 93).
Using
the estimated benefits and costs, the EcIS concludes
that level one measures
in total are clearly economically
feasible.
The total cost
is $311,000 while
the benefits range
from 1.3
to 1.5 million dollars.
The cost of the Peoria berms by
themselves
did not outweigh the benefits.
Insulation had an estimated cost of
$2 million against
benefits of $825,000.
However,
if the benefits of
reduced
heating and air conditioning costs
to homeowners are considered,
the cost would be
reduced to approximately one million dollars
and approach
a
1:1 benefit—cost ratio.
Similarly, noise
easements, which substitute compensation
for abatement, have
costs
equal to their benefits.
Property acquisitions were the
most expensive alternative at $29 million
in costs
to $825,000
in
benefits.
However, much of this cost could be recovered
if the
land were resold
for compatible uses.
The level
two and three curfew and reduced service options
had benefits of
between $2.2 million and $250,000 depending upon
the assumptions used
(Vol.
II at 96—112).
The costs could not be
reduced to dollar estimates.
The annual cost
of enforcement
including costs
to the
airports,
Illinois EPA, and this Board were estimated at $70,750
for the downstate facilities
(Vol.
II at 66).
69-173

—110—
The authors determined that the cost
of meeting the standard
could probably be recovered from
a small charge such as
a landing
fee:
For
illustration,
consider
an
abatement option
of
comparatively moderate
cost,
such
as
insulation.
If
undertaken
by
the
12
airport
authorities,
its
aggregate
cost
of
$2.0
million
(before
energy
savings)
might,
as
one
possibility,
be
recovered
through charges
in the
form
of
jet aircraft
landing
fees.
Suppose
recovery
took
place
over
a
5
year
period,
with a
flat
charge
on
each
jet
(air carrier
or
other)
landed.
Given
the volume
of operations at
these
airports,
such
a
charge
would
be
about
$5
per
landing.
This
charge
is
by no means negligible when
seen
as
an
increment
to
the
landing
fee
for
air
carriers
of
$24—$30
charged
by
many
airports,
or
to
the
parking
fee
of
$7
$10
charged ~to business
jets.
However,
the
$5
fee diminishes in
importance
when
put
on
a
per
passenger
basis.
Rough
calculations
indicate that
this
fee
amounts
to about
$0.25
per
passenger
landed.
assume
45
passengers
for Ozark
and
3 passengers
for business jets.
This
sum
is
substantially
less
than
1
of
the
typical
passenger
charge
for
an
Ozark
flight,
or
of
the
implicit
passenger
charge,or
cost
of
a
business
jet
flight.
The
$5
landing
charge
is
also
seen
to
be
small,
though
not
negligible,
when
compared
to
the
direct
operating
costs
(1978)
of
jet
aircraft
——
about
$9.50
per minute for DC—9 and $5.20 per minute
for
a business jet...
The
foregoing
observations
treat
costs
as
an
aggregate
for
the affected
airports.
But
it
should
be
noted
that
the
insulation
burden
is
not
evenly
distributed
among
these
airports.
The
Quad
Cities
airport
in particular has
a relatively large share
of
the dwellings eligible
for
insulation,
but
its share
of
air
traffic
is not commensurately as
large.
As
a
result,
insulation
costs,
if
recouped
in
landing
fees,
would
require
charges
of
around
2.5
times
as
great
as
those
indicated
above.
The
per passenger
cost
would
be
a
little
less
than
twice
the
earlier
figure
Vol.
II at 66—67.
As with the cost of flight rescheduling and reduction,
the
EcIS placed no dollar value on reducing the disruption in the
lives of
people living
in high noise areas.
O’Hare International
The discussion
of the economic reasonableness of the
proposed regulation as
it
relates to O’Hare and Midway airports
69-174

—111—
will be similar
to the discussion of the
twelve downstate
airports above.
The intensity of the surrounding land uses and
the numbers and types of aircraft operations at the two airports
complicates the analysis.
According to the authors,
In order
to reach compliance with
the 65 Ldn noise limit of the proposed regulation,
O’Hare would
have to implement the following changes
(retrofits and new, more
quiet aircraft already anticipated):
use
a quick clean up take-
off procedure,
use reduced flap landings
(federally required),
ban night flights without adding them
to the daytime traf1~ic
(Vol.
III
at
58, 62), with an overall
95 percent reduction
in
flights
(Vol.
IV at 80—2).
As for changing
to newer more quiet
aircraft,
the national fleet mix has been changing and already
is
85 percent
in compliance with FAR Part 36 requirements and will
be
in total compliance
in
a few years
See
September
18,
1985
testimony.
O’Hare’s fleet mix is assumed
to approximate the
national mix.
The quick clean up take—off procedure has already
been implemented.
Thus operational
cutbacks were considered
necessary
to meet the standard.
While Volume III spent
a lot of time on landing and take—off
procedures which are cost beneficial,
in view of the many changes
at O’Hare since
this EcIS was written,
this discussion will not
dwell on these
topics but will directly address operation
cutbacks.
As the authors of
the EcIS state, “it
is apparent
that enforcement of the regulation
to achieve compliance with the
prescribed noise limits would involve the implementation of
curfews and operations cutbacks.”
(Vol.
IV at iv).
Rather than
paraphrase the authors’ words concerning the economic impact of
the proposed regulation at O’Hare,
the Board will quote the
findings:
The
use
of
a
night)
curfew
at
O’Hare
would
affect up to 65,400 aircraft operations between 10:00
p.m. and 7:00 a.m. per annum.
The implications would
not
be
limited
to
aircraft
operations
alone.
More
specifically,
enforcement
of
this
scheme
would
eliminate
3,685,000
night
coach
fares.
Ancillary
effects
of
a
curfew
include passenger inconvenience,
reduced
efficiency
of
airline
operations,
cancellation and elimination of
flights and
a severe
adverse economic impact on air cargo transport.
The economic impacts of
imposing operations cuts
as
a means
of
reducing
noise
is
discussed
in
(Vol.
IV)
Section
H
(page 80).
The economic effects
of an
operations cutback would,
as the author notes,
“.
lead
to decreases
in direct
employment,
payrolls and
expenditures
for
local
goods and services by airport
tenants
sic,
resulting in, ultimately,
a variety of
indirect
and
induced
changes throughout
the
Chicago
area
economy.”
In
this
regard,
the
record
in these
proceedings
indicates
that
compliance
with
the
Ldn
69-175

—112—
noise
limit
would
result
in
a
direct
employment
decrease
of
over
11,600 with
a
commensurate payroll
reduction
of
$220,000,000.
The
latter would
induce
indirect
effects
on
employment
and
payroll
in
the
Chicago
area
by more
than 35,168,
with a payroll
of
$345,000,000.
Furthermore,
the
decrease
in
airport
related
expenditures
of
$194,000,000 translates
into
an indirect and induced decrease of $538.3 million.
Although
the
foregoing
discussion
alludes
to
differential
cost
and
benefits
projections,
the
economic
impacts
of
operations
cuts
as
a
means
to
achieve
compliance
with
the
proposed
regulations
is
substantial and readily quantifiable:
a reduction in
aircraft
operations
of
45
percent
to achieve
the
80
Ldn
noise
limit
would,
according
to
an
estimate
contained
in
Volume
IV,
reduce
employment
in
the
Chicago area economy by
a total of 49,000 jobs with
a
negative
economic
consequence
of
approximately
$2,000,000,000
on
the
regional
economy.
Vol.
IV at
iv—v; See Vol IV at 80—2,
87—89)
The first abatement strategy
(See Vol
IV, Table
III
7
at
151) considered involves
a quick flap retraction takeoff
procedure and change in the use of certain runways
at night,
thereby reducing noise levels at 101,500 homes by about 60
percent,
for
a total of
42,000 homes left above
65 Ldn.
Purchase of easements for the 42,000 homes,
based on certain
assumptions, would cost 113 million dollars, which
is
less costly
than insulation.
Insulation for these 42,000 homes would cost
210 million
to 341 million dollars without figuring the recovery
of heating and air conditioning costs, which may reduce these
figures
by half.
Acquisition and demolition of the same homes
cost approximately 2.7 billion dollars.
A total nighttime curfew wherein the flights are not added
to daytime operations would eliminate 10—12 percent of total
airport operations,
reducing by
40 percent the 42,000 homes
subjected to over 65 Ldn.
Before the imposition of any night
curfew there would
be 28,532 homes
in the 65—70 Ldn range, 10,607
in the 70—75 Ldn range,
2,046
in the 75—80 Ldn range and 760
in
the 80—85 Ldn range
(Vol.
IV, Table
111—6 at 145).
Once
a night
curfew was imposed, 24,651 homes would still
be over
65 Ldn and
are broken down
as follows:
16,434
(65—70 Ldn),
6,110
(70—75
Ldn),
1,536
(75—80 Ldn) and 571
(80—85 Ldn).
Id.
To bring the nearest residence to the airport down to 80
Ldn, however, further cuts would
be needed,
such as a 33 percent
reduction in daytime operations.
The cost for the night curfew
and 33 percent daytime
reduction is estimated at
2 billion
dollars
in aggregate expenditures and a loss of 49,000 jobs
in
the Chicago area economy.
69-176

—113—
Unfortunately,
the number
of homes subjected to over
65 Ldn
but which are then reduced by the
33 percent daytime operation
cut are not given.
Of course,
the number
of homes
further
reduced by a
33 percent day cut would not be as large
as the
number
from the night curfew due to the ten decibel weighting of
the night values and the absence of such weighting for day
values.
As
stated earlier,
for
total compliance with the final 65
Ldn noise limit of the proposed regulation using only operational
cuts,
95 percent of all operations at O’Hare would have
to be
eliminated.
Midway
Midway Airport and
its surrounding land uses are represented
in Figure
2—2 of Volume III.
The EcIS authors note that “the
airport
is not buffered at
its periphery by open space
or
by
commercial
or
industrial development.
Residential properties
abut the airport solidly to the west and south,
and somewhat
unevenly but still closely to the north and east.”
(Vol.
IV at
158).
The best data summation of the noise effects and contours of
Midway appears
in Volume IV and will
be duplicated here as Table
4.
Four different activity levels are represented by the data
in Table
4.
At the time of the EcIS preparation
(November
1981),
the authors chose
the 1977 representative noise levels and
discarded the 1979 option because of lack of data
(Vol.
IV at
159).
However,
it
is interesting
to note
that the 1979 data
shows
344 housing units
in the over 80 Ldn category and there
appear to be
85 Ldn pockets
(R.
6207).
As for lowering noise levels at Midway, modest operational
changes are not useful because of
residential density and runway
length
(Vol.
Iv at
158).
The lack of substantial nighttime
traffic lowers
the value of
a nighttime curfew
to almost
nothing.
Id.
As
in the other airport situations,
the alternative
mitigation options of easements, property acquisition,
insulation
and operation reductions were analyzed.
The results are
tabulated in Table IV—6
(Vol. IV at 178).
Easements on the average would cost $3,350 apiece and $27
million for the 8,000 dwelling units affected (Vol.
IV at 167).
Sixty percent would be
for
those dwellings
in the over 75 Ldn
contour.
Id.
The benefits
of noise easement purchase are equal
to
their costs.
69-177

—114—
TABLE
4
NOISE IMPACTS AT MIDWAY AIRPORT, CLASSIFIED BY DATA SOURCE
Data Source and Noise Level
Acres
Area
Population
Housing
Units
1.
1977 Master Plan contours,
320 daily departures
65—75 Ldn
Over
75 Ldn
1,280
640
20,000
7,000
6,000
2,000
2.
1995 Master Plan contours,
510 daily departures
65—75 Ldn
Over
75 Ldn
17,280
3,200
217,000
36,~000
65,000
11,000
3.
1979 Landrum and Brown
(Exhibit
51)
265
daily departures
Over
80 Ldn
n.a.
n.a.
344
4.
1985 Landrum and Brown
(Exhibit 53)
378 daily
departures
Over
65 Ldn
4,300
118,500
36,600
Sources:
(1) and
(2)
from “Airport Development Alternatives”,
Chicago O’Hare and Midway Master Plan Public
Information Meetings, November
6,
7 and 8, 1979.
Entries
(3)
and
(4)
are from the exhibits contained in
Testimony of
the City of Chicago Before the
Illinois
Pollution Control Board, June 16—20,
1980.
n.a.
is not available.
Excerpt
from EcIS Vol.
IV, Table
IV
1
at 160.
69-178

—115—
The acquisition and demolition of the 8,000 dwellings would
cost $423 million,
exceeding the benefits of $l3—27 million
(Vol.
IV at 168—9).
To purchase the 2,000 dwellings over
75 Ldn, costs
of $77 million are more than the benefits of $7—l6 million.
Id.
Insulation costs
for the 8,000 dwelling units above 65 Ldn
would be $7l—l02 million,
half of which would be for the 2,000
dwellings above
75
Ldn.
(Vol.
IV 163—6).
Once again,
calculation of energy savings could cut the costs
in half.
Despite this, the costs outweigh the benefits of $l7—27
million.
Id.
The benefits
in noise reduction to be achieved by operation
cutbacks would depend on the mix of jet and non—jet aircraft to
be eliminated or maintained.
One estimate
indicates that
a 97
percent cut
in operations would
be required from projected 1985
levels,
leaving twenty daily general aviation flights which would
include
a
few jet operations
(Vol.
IV at 170—172:
R. 6207).
To
achieve 80 Ldn rather than 65 Ldn at the nearest property would
require a 35—40 percent operations cut (VolIV at 172).
While no
costs
for operation reductions
(in order
to comply with
65 Ldn)
are given,
benefits to households and schools are estimated at
$28 million,
and when amortized over
10 years,
an average benefit
per day of $7,671 occurs
(Id. at 174—176).
The authors compare
the $7,671 benefit with
the impact of eliminating 620 operations.
‘a.
DISCUSSION
OF THE PROPOSED RULE
In considering this proposal, the Board has been impressed
by the complexity of the airport noise
issue.
The desires of the
competing interests are understandable and essentially preclude a
mutually satisfactory solution other than “airplanes that make no
noise”(R.
5808).
The Board agrees that the people subjected to noise need
relief and that efficient,
readily available air service
is
essential
to our
society.
The massive problem at O’Hare
and
Midway developed over
a number
of years and
it will take
a number
of years to bring
it under control.
At the downstate airports,
the problem is not
as severe and can be more readily be brought
under control.
Given
the planned expansion at downstate
airports, they too can expect to experience severe noise problems
in the absence of a noise regulation.
The Board agrees with Dr.
Zinschlag that “Charleston and Mattoon could become like
Bensenville
if something
is not done”
(R.
1815).
This Board by
itself cannot solve the noise problem.
Units
of federal,
state, and local government as well as the courts,
industry,
realtors, developers, proprietors and potential buyers
and sellers
of homes must all participate to some extent
if
progress
is
to be forthcoming.
For its part,
the Board will
establish
a noise standard for public airports and require that
cetain information be made available
to the public.
This action
69-179

—116—
by itself will make
a small, but hopefully significant, dent
in
a
very large problem.
The authority and ability to zone around
airports, develop and purchase quieter aircraft, alter
flight
operations and educate the public about potential noise problems
rests with other entities.
The Attorney General amended his proposal several times
since 1977.
The
following discussion is based on the proposal
filed on June
12, 1978
(Exh.
127)
as modified by AGO Comments of
October 26,
1983 and AGO Supplemental Comments of October
11,
1985.
The amendments of November 7,
1979
(Exh.
156) are not
being considered,
although they have not been formally
withdrawn.
The Board has modified the Attorney General’s
proposal
in several respects.
Comments on these modifications
and the basic rule are
requested during the first notice
period.
Portions of the proposed rule are discussed below.
Subpart
A:
General Provisions
Section 904.110
The definition of Class A land for purposes of this rule
is
that of Section 901.101 except that SLUCM codes 762 and 921 are
dropped.
This will allow flights
to use forest preserves and
some parks
as noise corridors.
The Board recognizes that while
parks should be noise impacted as
little as possible,
it
is far
more important
to protect Class A residential uses.
The forest
preserves around O’Hare provid& potential corridors for
routing
aircraft
to avoid residences.
The Board has included
in the
regulation definitions of
large, small,
public and civil aircraft which correspond
to those
of the FAA in the Title
14 of the Code of Federal Regulations.
The Board has simplified the definition of airport expansion
in proposed Section 904.110
to be the construction of
a new
runway.
The AGO’s definition
in its proposed rule 101(x)
(June
12, 1978 proposal) could
be interpreted
to
include any action
that increased the noise impact
of the airport.
Such all—
inclusive language could have had proprietors requesting
variances or
other relief every time
a flight pattern shifted or
another plane was added.
Section 904.120
The Board has incorporated 14 CFR 150, Appendix A (1985)
into the proposed rule.
This appendix is from the FAA’S Airport
Noise Compatibility Planning
rules.
It details the methods
for
calculating Ldn and developing noise exposure maps.
The use of
this appendix should make compliance less burdensome for airports
and consultants already familiar with the federal
methodologies.
FAR—iSO concepts are also used
in other portions
in the proposed rule.
It
is not the intent of the Board that all
provisions
of FAR—l50 apply to this rule.
In particular, noise
69-180

—117—
exposure maps developed
as part
of the federal Part 150 program
may be modified for use
in complying with the proposed rule.
Such maps may, however,
be used
in enforcement proceedings
against proprietors.
The proposed rule also specifies that the
maps contain some information
in
a form other than that required
by the FAR—150.
By incorporating Part 150,
the Board notes
that the FAA
Integrated Noise Model mentioned therein does not specify which
version
is to
be used.
The Board necessarily believes
the
current version
is to be used.
However,
to avoid confusion,
the
current version, Version
3,
will be used by the Board.
Therefore,
the Board hereby
introduces the following documents
into the record and adopts them as exhibits:
Exhibit
254:
FAA
Integrated
Noise
Model
Version
3
Users Guide;
* FAA—EE—B1—l7, October 1982,
as amended
by change
2
in August
1983.
Exhibit
255:
FAA
Integrated
Noise
Model
Validation:
Analysis of Carrier Flyovers at Seattle—
Tacoma Airport;
* FAA—EE—82—l9, November 1982.
Exhibit 254
is the user’s guide
for the current INM version and
Exhibit 255
is
its validation study.
Furthermore, the following technical documents utilized in
Part 150 Appendix A and which the Board has incorporated
in
Section 904.120 are made exhibits:
Exhibit
256:
“Methods
for
the Measurement
of
Sound
Levels,”
American
National
Standards
Institute
publication
ANSI
Sl.13—l971,
revised 1976,
available
from the American National Standards Institute,
Inc.,
1430 Broadway, New York, NY 10018;
Exhibit 257:
“Specification for Sound Level Meters,”
American
National
Standards
Institute
publication
ANSI
Sl.4—l983,
available
from
the
Standards
Secretariat,
Acoustical Society of America,
335
45th
Street, New York,
NY 10017.
The AGO suggested
in
its supplemental comments that the
following language be
included
in the rule:
To determine whether
emissions
of
sound
comply
with
this
Part,
Ldn
values
resulting
from
airport
operations
shall
be
determined
by
utilizing
any
of
the following procedures and methods of calculations:
(a)
“Calculations
of
Day—Night
Levels
(Ldn)
Resulting
from
Civil
Aircraft
Operations,”
January,
1977
(EPA 55019—77—450);
or
69-181

—118—
(b)
“Federal
Aviation
Administration
Integrated
Noise
Model,”
January,
1978
(FAA—EQ—78—0l),
as
from time to time
revised;
or
(C)
Any
Federal
Aviation
Administration
approved
methodology, such as those listed in
14 CFR Part
150,
Appendix
A,
and
as
from
time
to
time
revised; or
(d)
Any
procedure
adopted
by
the
Illinois
Environmental
Protection Agency
and
filed
with
the Illinois Secretary of State; or
(e)
Any other methodology demonstrated at hearing by
the
proponent
of
the
methodology
as
demonstrating
within
a
reasonable
degree
of
certainty
a
statistical
correlation
of
actual
with predicted
or measured aircraft noise levels
AGO
Supplemental Comments at
6
While these procedures may be useful, the Board notes that
most are not capable
of being incorporated into the
rule due to
the incorporation provisions
of the Illinois Administrative
Procedure Act (APA),
Ill.
Rev. Stat.
1985,
ch.
127,
par. 1006.02,
as amended
by P.A. 84—784
(eff.
January
1,
1986).
The APA provides that in any rule where there
is
incorporation of
a federal rule, standards or guidelines of a
federal agency or
of a nationally recognized organization or
association, that there be
no later amendments or editions
(Id.,
see also
1
Ill. Adm
.
Code 220.760, 220.780 as published at
9
Ill.
Reg.
20700, December
27,
1985).
The AGO’s language
in
subsections
(d) and
(e) would
be too speculative and could not be
used in any Illinois regulation.
The Board has accepted the
AGO’s
use
of 14 CFR Part 150 Appendix A and has also incorporated
two of
the standards/guidelines
of a nationally recognized
organization,
the American National Standards Institute.
The
Board
is confident that the procedure in Part 150 Appendix A as
proposed by the Board
in Section 904.120 will prove adequate.
Section 904.121
Proposed Section 904.121 specifies
the measurement and
documentation methods as well
as the equipment to be used
in this
Part.
The calculation of Ldn must be according to 14 CFR 150,
Appendix A (1985).
Section 904.122
Proposed Section 904.122 provides for
a violation
to be
shown by modeling.
While computer models are not 100 percent
accurate,
the Board accepts the reliability of
the INM and its
use as a practical enforcement tool,
which should not be
overlooked.
These modeled results are presumed
to be correct
69-182

—119—
unless rebutted by actual measurement data.
Any person seeking
to introduce actual measurement data must demonstrate its
statistical confidence
level as
to the average annual Ldn.
To be
admissible,
there must be 90 percent confidence that the
measurement
is within 1.5 dB of the annual average Ldn.
With the
possibility
of both types of data being used,
a more fair system
of enforcement will exist
than
if only one type of data were
allowed.
The complainant has the burden of establishing a
violation.
Section 904.123
This
is
a standard severability section,
and has been added
in the event that any portion of the rule is adjudged invalid
outright or
as applied to any person.
SubEart B:
Prohibitions
Section 904.201
The questions of airport expansion before the implementation
of the final
65 Ldn standard has troubled this proceeding from
the start.
The original proposal defined
“airport expansion”
as
follows:
Any
change
in
or
modification
to
airport
property
or
airport
operations,
including
but
not
limited
to
type
and
number
of
aircraft
and
aircraft
operating procedures,
that increases the noise impact
of the airport.
In the context of
the rule as
then proposed, this would prohibit
almost any change in operations by even one plane that exposed
additional Class A land
to noise
in excess
of
65 Ldn, even
if 80
Ldn was the current standard for previously exposed land.
Simply
put, adoption of the original
rule would lead
to innumerable
enforcement cases or proprietors seeking variances for simple
operational changes.
In its 1983 comments,
the AGO attempted to address this
problem by limiting the meaning of the term “expansion”
as used
in its original rule:
Rule
502
Section
904.201
should
clarify
that
“expansion”
refers
to
physical
expansion,
requiring
the
construction
or
alteration
of
facilities
that
have
the
potential
to signficantiy
increase
airport
operations.
Examples
would
include
the constructin
of
new
runways,
runway
extensions,
taxiways,
gates,
strengthening
of
existing
runways
to
allow
utilization
by
larger
aircraft, and
the installation
of
navigation
aids;
in
addition,
airport
projects
which would qualify
for
(but not necessarily receive
in
fact)
funding under federal grant agreements, such
69-183

—120—
as
those
administered under
the
Federal Airport Act,
49
U.S.C.
Section
1101,
et
seq.,
or
the Airport and
Airway
Development
Act
of
1970,
49
U.S.C.
Section
1701,
et
seq.,
should
normally
also
be
included
as
examples.
Confusion
may
also
be
associated
with
the
exclusion
of
Class
A
land which
has previously been
subjected
to
levels
of
noise
in
excess
of
Ldn
65
dB.
At
O’Hare,
for
example,
the
Ldn
65
dB
noise
contours
are
retracting,
and
there
are many Class
A
properties
which
have
previously
been
subjected
to
Ldn 65 dB.
Determining which properties have or have
not
fallen
mo
this
category
is
difficult,
if
not
impossible.
The
language
of
Rule
502
should
be
modified
to establish the Ldn
65 dB contour depicting
“existing conditions”
at
the
time of
the adoption of
the
regulations
as
the
reference
contour
for
determining
which
Class
A
land
areas
have
been
“previously exposed”
Comments,
21 and 22.
In 1985, the AGO further modified the definition,
again
without providing specific language:
The AGO therefore believes that any action taken
by
an airport proprietor that results
in
a
reduction
of
total
population
impacted
by Ldn levels
in excess
of
65 Ldn would not amount
to an “airport expansion”
(and
be
an
acceptable
variance
compliance
program)
even
if,
as a result of such action, Class A land not
previously subject to Ldn levels
in excess of 65 Ldn,
were
then
subjected
to
levels
in
excess
of
65
Ldn,
provided
that
no
Class
A
land
use
that
was
not
previously
exposed
to
75
Ldn
or
greater
levels
AGO
Supplemental Comments at 7).
The Board believes that even this current suggestion will
lead to confusion.
Much time and resources would be required to
determine the extent of prior
noise contours and numerous
variances would be sought
to protect proprietors.
These
resources will
be better utilized
if focused on compliance
efforts.
In defining expansion as
the construction of
a new runway,
the Board notes that its definition allows runway lengthening and
other improvements at existing airports without such improvements
being classified as expansion.
Proprietors should be aware
that
if they unreasonably subject additional persons to excessive
noise during the phase
in period, by taking undue advantage of
this definition,
they may be found
to have created a self—imposed
hardship in future proceedings.
Given that the airport noise
standard will reach 65 Ldn
in 1994,
the difference between the
standards
in 904.201 and 904.202 will
be short—lived.
69-184

—121—
Section 904.202
The AGO established
a noise standard that would be gradually
phased
in.
It was
to begin at 80 Ldn six months after adoption
of
the rule and reach 65 Ldn after
seven years.
The Board
proposes
to set an
80 Ldn standard beginning approximately 18
months after adoption.
It will reach 75 Ldn about
18 months
later and 65 Ldn about eight years after adoption.
The dates
in
Section 904.202 will be adjusted at final notice to reflect these
intervals and begin
on calendar quarters.
The additional year
is necessary
to allow proprietors time
to determine their
noise contours and develop noise abatement
plans.
It
is unreasonable
to expect all airports
in the state
to
be able
to retain consultants and meet the standard or seek
a
variance or exception within six months of adoption.
The added
time will also allow the Agency
to prepare for any role
it seeks
to play
in monitoring airport noise and enforcing the
regulation.
This
is particularly necesary in light of the Agency
comment presented at the supplemental hearing:
...As
you
are
aware,
the
Agency’s
noise
pollution
division
has
been
disbanded
for
a
number
of
years
because
it failed to receive funding from the General
Assembly.
Therefore,
the Agency has not been able
to
maintain a full—time staff for inspections of sources
of
noise
pollution.
The
~gency has
tried
to
be
as
responsive
as
possible
to
citizens
with
noise
complaints
by conducting
inspections with several
of
the
former
noise
division
staff
who
are
still
with
the Agency
in other positions.
Due
to
the
displacement
of
the
noise
program
within
the Agency,
we would
be unable
at the current
time to adequately enforce the proposed rule, monitor
noise
levels,
or
set
procedural
standards
for
monitoring
noise levels
Exh.
230.
Subpart C:
Data Collection and Reporting
Section 904.301
As suggested
in the AGO’s supplemental comments, Section
904.301 provides that proprietors shall record the data for jet
aircraft operations required
to code and run the FAA Integrated
Noise
Model.
These records will
be submitted to the Agency and
be available for public inspection.
The system
is similar to the
discharge monitoring reports currently filed with the Agency by
operators of wastewater treatment plants.
Such
a system will
insure that other parties can check the noise exposure maps
provided by the proprietor.
The original proposal provided that
the information be submitted
to the Agency monthly.
The Board
believes that quarterly reporting will be adequate and will
reduce the administrative burden.
69-185

—122—
Section 904.302
Rule 505 of the original proposal contained
a detailed
variance procedure which included the development of maps showing
noise impacted areas and a plan to reduce
the noise impacts.
The
proposed rule does not contain specific variance language because
variances are adequately provided for
in the Act.
However,
much
of the thrust of rule 505 has been adopted for use
in the
Adjusted Standard Provision
of Subpart
E.
The rule 505 map
concept has been used in Section 904.302 which requires the
development of noise exposure maps.
The noise exposure maps will provide local officials with
information on the location of areas exposed
to high noise
levels.
The record clearly shows that without this information,
they have difficulty planning future development to avoid noisy
areas.
The availability of
this information
in the hands of
prudent planners and developers should help prevent downstate
airports from falling into the dilemma now faced by O’Hare and
Midway.
Section 904.303
The required noise exposure maps
are
to be developed
according
to the FAR—l50 methodologies.
This will allow airports
and their consultants to utilize material developed pursuant to
FAA
requirements
to help meet the provisions of this
regulation.
The maps
shall contain at
a minimum the data and
features listed
in 904.302.
These differ
from those
in 14 CFR
Section Al50.lol
in some respects.
Up
to three separate noise maps may be submitted by a
proprietor under Section 904.303.
A noise exposure map showing
the impact of all operations must be submitted.
Airports with
significant military operations may provide a map showing what
the noise contours wuld
be without military flights.
This may
prove important
to proprietors since
noise from military aircraft
is not
to be considered when determining compliance with the
standard.
A third map may be prepared detailing the noise
contours that are expected
to result from airport expansion or
operational changes.
The Board intends
that these maps
be
readily available to public officials,
developers and the public
at large.
The requirements
for distribution
to the Agency,
counties and municipalities and the publication of their
availability at the airport are minimal.
Subpart D:
Exceptions
Section 904.401
Proposed section 904.401 essentially echoes the AGO’s
proposed rule 506
(See June 12,
1978 proposal) and
is similar
to
FAR—l50.
A proprietor
is exempt from any violations as
to any
69- 186

—123—
Class A land that was not Class A land at the time of
the filing
and submission of the noise exposure map by the proprietor,
was
shown on the map and the proprietor made an effort to persuade
the local
zoning authority not
to change
a non—Class A to a Class
A land use.
This exemption provides protection
for the
proprietor against local governmental authorities who,
for one
reason or another, have resisted preventing Class A land uses
in
noise impacted areas where such uses were not located before.
A further exemption
is available
if the proprietor buys
a
noise easement or equivalent interest over Class A land, provided
that any such noise easement would not exempt a proprietor from
violation
if the Class A land
is subject to
75 Ldn or greater.
This limit on the noise easement exemption provides greater
protection of the public living
in heavily noise impacted
areas.
It
is consistent with the studies which conclude
that
exposure
to 75 Ldn
is totally unacceptable for residential use
and
was suggested by the AGO.
Section 904.402
While proposed Section 904.402 requires the collection and
reporting of military aircraft noise data, such noise data
is not
considered when determining whether a proprietor
is
in
compliance.
The proprietor has no control over military aircraft
and should not be penalized for airport noise emitted by military
aircraft.
This
lack of control does not relieve the proprietor
from the collection and reporting requirements.
Subpart
E:
Adjusted Standards Procedures
Section 904.504
Under the Act,
the Board may grant
a variance to a person
who would suffer
an arbitrary or unreasonable hardship if forced
to immediately comply with
a regulation.
A variance has
a five
year
limit and requires ultimate compliance.
In addition the Act
provides for permanent site specific relief from a regulation.
However
the Board realizes that a perpetual site specific rule
would be inappropriate
in many circumstances given the potential
changes
in
technology and operations which are described in the
record.
Given
this situation,
the Board has developed an
adjusted standards procedure for airport noise pursuant to
Section 28.1 of the Act.
The record makes
clear
that the AGO intends
that proprietors
who cannot meet the initial timeframes
be given an opportunity
to
seek relief
from the standard.
AGO witness Galloway agreed that
rational use of O’Hare would not permit
it to achieve the 65 Ldn
limit by the year 2000
(R.
at 5712).
Assistant Attorney General
Blackwood also spoke to this point:
The
proposed
regulation
requires him
to
study
the problem and
———
in
the context
of
applying
for
a
69-187

—124—
variance.
They will require him to study the problem
at
his
airport
and
implement
whatever
he
can
implement
which
is
within
———
which
is
feasible
to
implement.
In
other
words,
to
do
the
best
he
can
do,
whatever
that
may
be,
and
that
obviously
is
a
different proposition at different airports.
At
some
airports,
he
can
impose
types
of
limitations
feasibly which
would
not be
feasible
at
other airports, but he should look at
it and do it if
he
can.
I
think
it’s
really no different
than
the
kind
of
thing
the
Board considers
in
other
variance
applications
of
———
if
compliance
with
the standard
is
not
immediately
feasible,
then
a
variance can
be
issued based upon conditions,
in effect,
a compliance
plan.
A
plan
to
do
what
can
be
done
and
leading
toward compliance at some future data (R.~2895).
The Board envisions
a number of situations where an adjusted
standard may prove useful and save considerable time and
effort.
One such example might involve a small airport with very
few jet operations,
a limited budget, and no Class A land within
miles.
The proprietor may propose a proceedure
for submitting
a
map with noise contours calculated by one of
the non—computerized
method referred to
in the record and not reporting operations
until a certain number of operations per day
is reached.
He
might attempt
to justify the proposed proceedure by demonstrating
that much
of the analysis required by Section 904.504 would serve
no useful purpose given the facts of his
situation.
A petitioner
seeking an adjusted standard must provide enough
information to
justify any request.
The Board does not intend to make
assumptions
to fill data gaps
in petitions.
Section 904.504(a)
and
(b)
list
a minimum of
13 noise
reduction options that
a proprietor
should evaluate when seeking
an adjusted standard.
They are drawn from a list contained in
the original proposal except that Part
36 considerations have
been dropped.
The Board
is aware that
a proprietor acting alone
cannot implement all
of the possible noise abatement options.
It
is also true that some are simply inapplicable to certain
airports.
Some options require the approval
or cooperation
of
the FAA,
an aircraft operator,
local governmental unit or private
landowner.
The Board does not expect that the discussion of each
option be accompanied by an expensive an highly detailed
consultant’s analysis.
it
is apparent,
for example,
that some
airports will have far more to present under 904.504(b)
concerning preferential runways than others.
The Board does
expect enough credible information
to support the petitioner’s
conclusion and allow the Board
to reach
a reasoned decision.
The noise abatement plan
in 904.504
(c)
is expected
to lead
to a reduction in noise impact over time.
The Board realizes
69.188

—125—
that solutions will not develop overnight.
An adjusted standard
petition might,
for example,
involve a plan that incorportes
a
zoning authority’s promise
to prohibit sensitive development
in
high noise areas,
an operators agreement not to fly
over
a nearby
city,
the acquisition of some impacted homes over
a
ten year
period using
funds generated by a landing fee,
shielding
a
maintenance facility and extending
the implementation date
of
the
65 Ldn standard by ten years.
The intent
of subsection 904.504(d)
is to allow petitioners
the chance
to avoid the time and expense of studying in depth
options that will provide little or
no noise abatement or
are not
practical
at the airport
in question.
Petitioners should be
aware
that
they may
be asked
to provide more information or
attend additional hearings
if the Board finds or
is given reason
to believe that the analysis provided
is inadequate.
IT
IS SO ORDERED.
B.S.
Forcade dissented, W.J. Nega concurred and J.T.
Meyer
abstained.
I, Dorothy
M. Gunn,
Clerk
of the Illinois Pollution Control
Board, hereby certify that the above Proposed Opinion was adopted
on
the
/~‘~Z~
day
of
___________________,
1986 by
a
vote of
.~—/
.
7~.
Dorothy M.
unn, Clerk
Illinois Pollution Control Board
69-189

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