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ACRP Report 15: Aircraft Noise: A Toolkit for Managing Community Expectations (2010)
Airport Cooperative Research Program (ACRP)

Citation Manager

Woodward, Jon M, Briscoe, Lisa Lassman, Dunholter, Paul, Transportation Research Board. "Number of Events Above (NA)." ACRP Report 15: Aircraft Noise: A Toolkit for Managing Community Expectations. Washington, DC: The National Academies Press, 2010.

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Page
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Front Matter (R1-R12)
Chapter 1 - Introduction and Guidebook Summary (1-1)
How to Use the Guidebook (2-2)
The Relationship Between Environmental Planning for Airports and General Community Response Factors (3-3)
Culture Shift Required (4-5)
Select Staff for Service-Oriented Attitude (People-Skills) (6-6)
Cumulative versus Single Event Noise (7-7)
Best Practices for Managing Noise Compatibility Issues (8-9)
Legal/Administrative Requirements for Public Contact (10-10)
Shifting to a Public Service-Oriented Approach (11-11)
Potential Communication Objectives (12-12)
Example Evaluation Questions (13-13)
What Does the Public Really Want? (14-14)
Introduction (15-15)
Strategies for Successful Community Engagement (16-16)
Strategies for Successful Community Engagement (17-26)
Self-Assessment Tool (27-27)
How to Use the Self-Assessment Tool (28-31)
Implementation Steps Matrix (32-32)
How to Use the Implementation Steps Matrix (33-35)
Community Engagement Techniques and Tools (36-36)
Community Involvement Manuals (37-37)
Communications Checklists (38-39)
Checklists For Meeting Preparation and Meeting Announcements (40-40)
Brochures (41-42)
Fact Sheets (43-43)
Flyers or Posters (44-44)
Newsletters (45-45)
Frequently Asked Questions (46-46)
Annual Reports and Noise Program Overviews (47-48)
Multimedia Presentations (49-50)
Websites (51-51)
Interactive Learning Tool (52-53)
Advanced Technology Demonstrations (54-54)
Outreach Vehicle Tools (55-55)
Airport and Peer Industry Literature Review (56-56)
Airport Case Studies (57-57)
University Case Study (58-58)
Best Practices in the Airport Industry: An Assessment of Airport Community Involvement Efforts (59-60)
Best Practices in the Transportation Industry: Transportation Research Board White Paper (61-61)
What is Good Practice? (62-62)
Challenges to Practitioners: Areas for Development (63-63)
Conclusions (64-64)
Study Findings (65-66)
Large/Medium-Hub Airport with Passenger Service - San Francisco International Airport (SFO) (67-69)
Small/Non-Hub Airport with Passenger Service - Long Beach Airport (LGB) (70-72)
Cargo Hub Airport - Louisville International Airport/Standiford Field (SDF) (73-75)
Large General Aviation/Reliever Airport - Van Nuys Airport (VNY) (76-79)
Smaller General Aviation Airport - Ohio State University Airport (OSU) (80-81)
Education Industry - Crisis in the College/University Relationship with the Community: A Case Study (14) (82-84)
Conclusions (85-86)
Chapter 6 - Noise Management and Public Response (87-87)
Congressional and Federal Regulatory Actions (88-89)
FAA Orders and Guidance on Environmental Planning (90-90)
State and Local Action (91-91)
Airport Role in Comprehensive Planning (92-92)
Stakeholder Involvement and Jurisdictional Coordination (93-93)
Cumulative versus Single Event Noise Levels (94-94)
Thresholds of Significant Noise (95-99)
Difference Between Compatible and Incompatible (Noise-Sensitive) Land Uses (100-100)
Differences within the FAA Divisions Regarding Thresholds of Noise Level Evaluation (60/65 DNL in Airports vs. 45/60/65 DNL in Air Traffic) (101-101)
Precedence of Federal and State/Local Standards and When Applicable (102-103)
Measured versus Computer-Modeled Noise Levels (104-104)
Sound Insulation Programs for Noise Abatement (105-106)
Difference between Interior and Exterior Sound Levels and Methods to Abate Each (107-107)
Contour and Impact Area Change Over Time and the Differences Between Federal and Local Response to Change (108-108)
Self Assessment Tools for Noise Management Programs (109-109)
Evaluation Checklist for Airports with Established Noise Programs (110-110)
Chapter 7 - Noise Metrics and Community Response (111-111)
Cumulative Noise Metrics (112-112)
Community Noise Equivalent Level (CNEL) (113-113)
Sound Exposure Level (SEL) (114-114)
Maximum A-Weighted Sound Level (Lmax) (115-115)
Number of Events Above (NA) (116-116)
Time Above (117-117)
Best Applications (118-118)
Noise Complaint Characteristics (119-121)
Preferential Runway Use Program (122-122)
Flight Track Modifications to Fly Over Compatible Uses (123-123)
Approach Thrust and Flap Management Procedures (124-124)
Restrict Ground Run-up Activity (125-125)
Displaced Threshold - Landings (126-126)
High Speed Exit Taxiways (127-127)
Enhanced Navigational Aids (128-128)
Airport Access Restrictions (129-130)
Best Practices (131-132)
Chapter 9 - Land Use Management Techniques for Noise Abatement (133-133)
Purchase of Non-Compatible Land (134-134)
Waiver of Claim (135-135)
Purchase Assurance/Sales Assistance (136-136)
Comprehensive Community Planning (137-137)
Noise Impact Overlay Zoning (138-138)
Dedication of Noise and Overflight Easements (139-139)
Development Density Restrictions in High Noise Areas (140-140)
Building Code Modifications (141-141)
Best Practices in Land Use Management for Noise Compatibility (142-143)
References (144-151)
Abbreviations used without definitions in TRB publications (152-152)

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116 Aircraft Noise: A Toolkit for Managing Community Expectations Slant Range Distance/Altitude Another factor frequently cited by the public as a noise issue is the distance from the aircraft in flight to the listener on the ground (the slant/range distance) or the aircraft's altitude. The slant/range distance represents the hypotenuse of a triangle formed by the aircraft altitude and the lateral distance from the ground location to the point of closest approach along an aircraft's path of flight. Noise complaints recorded by those airports surveyed for this evaluation cited "too low" as a common source of public concern. Similarly, the public will often be aware of preferred flight patterns and complain that the air- craft was "right over my house" and frequently point to a location halfway above the horizon instead of straight up. The perception of location, coupled with distance, is often difficult to answer without the use of triangulation. An aircraft 45 degrees above the horizon is as far away horizontally as it is vertically and farther than either when measured in a straight line distance. Members of the public often are interested in the number of events that overfly an area at dif- ferent altitudes and may request that altitudes be raised to abate noise. As the distance between the noise source and the receiver is increased, the noise level will decrease by six decibels with every doubling of distance. Consequently, a noise event of 80 dBA of SEL at 3,000 feet overhead will be decreased to 74 dBA of SEL if the altitude of the aircraft is increased to 6,000 feet. It is often very difficult to increase aircraft altitudes by significant amounts at any course along a flight track without adding substantial length to the track prior to passing over, or in some cases, with- out significantly increasing the power setting used in flight (and the resulting noise level). However, if the same flight track were relocated laterally by one mile, the noise reduction would be the same because the distance between the source and the receiver would be increased to 6,000 feet. It is often much easier to relocate a flight track than to increase altitude enough to achieve a meaningful reduction in single event noise levels. Hybrid Metrics As information has become more available for individual aircraft types, as noise prediction tools have been improved, and as the public has become more sophisticated in their understand- ing of the effects and consequences of aircraft development actions, new applications of avail- able metrics have evolved to be more responsive to public interests. Several supplemental metrics have evolved in recent years that allow the noise analyst to develop information that may be more meaningful to members of the public in their understanding of aviation noise. While such sup- plemental metrics are not required for inclusion in any environmental evaluation, their avail- ability is well known and often advisable at locations where noise is a contentious issue. These metrics are typically formed from combinations of simpler single event metrics. Because they are developed from more detailed computer modeling and post-processing requirements than the more standard metrics described in earlier sections, they are more costly to produce. They include Number of Events Above, Time Above, and Audibility. Number of Events Above (NA) In recent years, the Number of Events Above metric has become popular as a means of com- paring the number of operations above various thresholds of loudness associated with opera- tional alternatives. The INM is capable of computing the SEL or Lmax of every operation that is included in its input data, at any location selected by the program's user. The availability of this information will allow the noise analyst to sort output data to provide the numbers of daily operations that exceed selected noise thresholds. For example, the number of flights exceed-