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