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

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Woodward, Jon M, Briscoe, Lisa Lassman, Dunholter, Paul, Transportation Research Board. "Maximum A-Weighted Sound Level (Lmax)." 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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Noise Metrics and Community Response 115 Figure 7-2. Comparative single event noise metrics compared to equivalent noise level. while clearly accounting for both their peak noise levels and durations. For example, the same operation may be considered along an existing and proposed flight track. The SEL of each oper- ation would be compared to provide insight into the prospective effects of changing location on the underlying population. Further, the SEL is the preferred metric for the evaluation of sleep disturbance, making it critical to the evaluation of noise abatement measures that are directed at night operations. Typically, the SEL is approximately 8-10 decibels louder than the peak noise level that occurs during a single event. The SEL is represented by a series of dark bars and compared to the measured noise levels, including Lmax, through the course of several single events in Figure 7-2. Example of Metric Display for Public Information: · Example of SEL computation Video: (prepared for ACRP 02-05 project) 7-6 Maximum A-Weighted Sound Level (Lmax) The Lmax of an event represents the loudest decibel level achieved during that event. It also can be expressed over a period of time (hour, day, year, etc.). Similar to SEL, the metric is useful to compare operational alternatives for noise abatement. Unlike SEL, it is not subject to the com- pression of all noise energy during an event into a single second, but rather provides the instan- taneous peak noise level achieved. Consequently, it is the loudest aircraft noise level the public experiences, and often the one most cited in public comment and complaint. Example of metric display for public information: · Comparison of Sound ­ Outdoor and Indoor sound levels (157) 7-7 · ORD Aircraft Noise Comparison (single event footprints) (158) 7-8 · Loudest Aircraft Noise Events Site Report (Chicago O'Hare) (159) 7-9 · Example of Lmax computation Video (prepared for ACRP 02-05 project) 7-10