Acoustics - Description, measurement and assessment of environmental noise - Part 3: Objective method for the measurement of prominence of impulsive sounds and for adjustment of L Aeq

This method objectively categorises sources by determination of the prominence of impulsive sound, with the aim of correlating to community response. This method for measuring the prominence of impulsive sounds is intended for sources not identified as gunfire or high-energy impulsive sound. It typically produces adjustments in the range 0,0 dB to 9,0 dB. These adjustments are intended to be used to categorise the sources as either regular impulsive or highly impulsive sound sources and apply the penalty indicated in ISO 1996-1. However, the adjustments may be applied directly, as is done in NT ACOU 112[2], and BS 4142[3]. ISO 1996-2 provides additional guidance for performing these measurements. The method is intended for use on sources with impulsive characteristics that are not already categorised in ISO 1996-1. A non-exhaustive list of examples includes compressed air release, scrap handling, goods delivery, fork lifts with rattling forks, skateboard ramps, industrial shearing, gas discharges, percussive tools in demolition, powered riveting, etc. The method is not intended for use on sounds from firearms. Although the measurements of prominence may give relevant results, research has shown the response to these sources is influenced by factors outside of the scope of this document. In addition, the method is not intended to use for high-energy impulsive sound sources as specified in ISO 1996-1. NOTE This method is not intended for occupational hearing loss, which is outside the scope of this document. See Annex A for recommended additional research.

Acoustique — Description, mesurage et évaluation du bruit de l'environnement — Partie 3: Méthode objective pour le mesurage de l’émergence des bruits impulsifs et pour l’ajustement du L Aeq

General Information

Status
Published
Publication Date
05-Jul-2022
Current Stage
9093 - International Standard confirmed
Start Date
17-Dec-2025
Completion Date
27-Dec-2025
Ref Project

Overview

ISO/PAS 1996-3:2022 - "Acoustics - Description, measurement and assessment of environmental noise - Part 3" defines an objective method to measure the prominence of impulsive sounds and to determine an adjustment to L_Aeq (equivalent continuous A-weighted sound level). The method is intended to correlate measured impulsive characteristics with community response for environmental noise assessment. It is not intended for firearms, high‑energy impulsive sources (per ISO 1996‑1) or occupational hearing-loss assessments.

Key topics and technical requirements

  • Prominence (P): An index combining the impulse onset rate and level difference to quantify how prominent an impulse is at the receiver. The general form is P = k1·log(onset rate) + k2·log(level difference); constants are derived from listening tests.
  • Onset rate and level difference: Onset rate (OR) is calculated from the slope of the A‑weighted, F‑time-weighted level (threshold: gradients ≥ 10 dB/s define an onset). Level difference (LD) is the difference between onset start and end.
  • Measurement instrumentation: Uses Class 1 sound level meters (IEC 61672‑1) with logged A‑weighted, F‑time‑weighted samples. Preferred sampling interval is 10–25 ms; 100 ms is allowed for screening with higher uncertainty.
  • Assessment time interval: Default is 30 minutes. The impulse with the highest P during each interval provides the adjustment for that interval; reference-time ratings are energy-averages of assessment intervals.
  • Adjustment to L_Aeq: The standard defines how to convert prominence into a penalty/adjustment applied to L_Aeq (typical adjustments are in the range 0.0 dB to 9.0 dB). These adjustments are used to categorise sources (regular impulsive vs. highly impulsive) per ISO 1996‑1, or may be applied directly as in some national methods.
  • Data handling: Guidance on excluding residual-source impulses, use of audio recording for unattended surveys, and reporting requirements is included.
  • Research guidance: Annex A lists recommended research topics where further work is needed.

Practical applications

  • Quantifying impulsive environmental noise from industrial processes, goods handling, demolition tools, compressed-air releases, skateboard ramps, powered riveting, fork lifts, etc.
  • Providing an objective basis for applying impulsivity penalties to L_Aeq in environmental noise assessments, planning decisions, nuisance investigations, and impact assessments.
  • Supporting noise mitigation planning, regulatory enforcement and community response studies by linking measurable impulse characteristics to annoyance.

Who should use this standard

  • Acoustical consultants and environmental noise specialists
  • Local authorities and planning regulators
  • Industrial noise control engineers and site operators
  • Researchers studying noise annoyance and impulsive sound metrics

Related standards

  • ISO 1996‑1 (basic quantities and assessment procedures)
  • ISO 1996‑2 (measurement guidance)
  • IEC 61672‑1 (sound level meter specifications)
  • Related national methods: BS 4142, NT ACOU 112

Keywords: ISO 1996-3:2022, environmental noise, impulsive sounds, prominence, L_Aeq adjustment, onset rate, level difference, sound level meter, Class 1.

Technical specification
ISO/PAS 1996-3:2022 - Acoustics — Description, measurement and assessment of environmental noise — Part 3: Objective method for the measurement of prominence of impulsive sounds and for adjustment of L Aeq Released:6. 07. 2022
English language
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Frequently Asked Questions

ISO/PAS 1996-3:2022 is a technical specification published by the International Organization for Standardization (ISO). Its full title is "Acoustics - Description, measurement and assessment of environmental noise - Part 3: Objective method for the measurement of prominence of impulsive sounds and for adjustment of L Aeq". This standard covers: This method objectively categorises sources by determination of the prominence of impulsive sound, with the aim of correlating to community response. This method for measuring the prominence of impulsive sounds is intended for sources not identified as gunfire or high-energy impulsive sound. It typically produces adjustments in the range 0,0 dB to 9,0 dB. These adjustments are intended to be used to categorise the sources as either regular impulsive or highly impulsive sound sources and apply the penalty indicated in ISO 1996-1. However, the adjustments may be applied directly, as is done in NT ACOU 112[2], and BS 4142[3]. ISO 1996-2 provides additional guidance for performing these measurements. The method is intended for use on sources with impulsive characteristics that are not already categorised in ISO 1996-1. A non-exhaustive list of examples includes compressed air release, scrap handling, goods delivery, fork lifts with rattling forks, skateboard ramps, industrial shearing, gas discharges, percussive tools in demolition, powered riveting, etc. The method is not intended for use on sounds from firearms. Although the measurements of prominence may give relevant results, research has shown the response to these sources is influenced by factors outside of the scope of this document. In addition, the method is not intended to use for high-energy impulsive sound sources as specified in ISO 1996-1. NOTE This method is not intended for occupational hearing loss, which is outside the scope of this document. See Annex A for recommended additional research.

This method objectively categorises sources by determination of the prominence of impulsive sound, with the aim of correlating to community response. This method for measuring the prominence of impulsive sounds is intended for sources not identified as gunfire or high-energy impulsive sound. It typically produces adjustments in the range 0,0 dB to 9,0 dB. These adjustments are intended to be used to categorise the sources as either regular impulsive or highly impulsive sound sources and apply the penalty indicated in ISO 1996-1. However, the adjustments may be applied directly, as is done in NT ACOU 112[2], and BS 4142[3]. ISO 1996-2 provides additional guidance for performing these measurements. The method is intended for use on sources with impulsive characteristics that are not already categorised in ISO 1996-1. A non-exhaustive list of examples includes compressed air release, scrap handling, goods delivery, fork lifts with rattling forks, skateboard ramps, industrial shearing, gas discharges, percussive tools in demolition, powered riveting, etc. The method is not intended for use on sounds from firearms. Although the measurements of prominence may give relevant results, research has shown the response to these sources is influenced by factors outside of the scope of this document. In addition, the method is not intended to use for high-energy impulsive sound sources as specified in ISO 1996-1. NOTE This method is not intended for occupational hearing loss, which is outside the scope of this document. See Annex A for recommended additional research.

ISO/PAS 1996-3:2022 is classified under the following ICS (International Classification for Standards) categories: 13.140 - Noise with respect to human beings; 17.140.01 - Acoustic measurements and noise abatement in general. The ICS classification helps identify the subject area and facilitates finding related standards.

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Standards Content (Sample)


PUBLICLY ISO/PAS
AVAILABLE 1996-3
SPECIFICATION
First edition
2022-07
Acoustics — Description,
measurement and assessment of
environmental noise —
Part 3:
Objective method for the
measurement of prominence of
impulsive sounds and for adjustment
of L
Aeq
Acoustique — Description, mesurage et évaluation du bruit de
l'environnement —
Partie 3: Méthode objective pour le mesurage de l’émergence des
bruits impulsifs et pour l’ajustement du L
Aeq
Reference number
© ISO 2022
All rights reserved. Unless otherwise specified, or required in the context of its implementation, no part of this publication may
be reproduced or utilized otherwise in any form or by any means, electronic or mechanical, including photocopying, or posting on
the internet or an intranet, without prior written permission. Permission can be requested from either ISO at the address below
or ISO’s member body in the country of the requester.
ISO copyright office
CP 401 • Ch. de Blandonnet 8
CH-1214 Vernier, Geneva
Phone: +41 22 749 01 11
Email: copyright@iso.org
Website: www.iso.org
Published in Switzerland
ii
Contents Page
Foreword .iv
Introduction .v
1 Scope . 1
2 Normative references . 1
3 Terms and definitions . 1
4 Measurements .3
5 Prominence, P . . 5
6 Identification of adjustment to L . 6
Aeq
7 Categorisation of impulsive sound .7
8 Accuracy . 7
9 Test report . 7
Annex A (informative) Research topics . 8
Bibliography . 9
iii
Foreword
ISO (the International Organization for Standardization) is a worldwide federation of national standards
bodies (ISO member bodies). The work of preparing International Standards is normally carried out
through ISO technical committees. Each member body interested in a subject for which a technical
committee has been established has the right to be represented on that committee. International
organizations, governmental and non-governmental, in liaison with ISO, also take part in the work.
ISO collaborates closely with the International Electrotechnical Commission (IEC) on all matters of
electrotechnical standardization.
The procedures used to develop this document and those intended for its further maintenance are
described in the ISO/IEC Directives, Part 1. In particular, the different approval criteria needed for the
different types of ISO documents should be noted. This document was drafted in accordance with the
editorial rules of the ISO/IEC Directives, Part 2 (see www.iso.org/directives).
Attention is drawn to the possibility that some of the elements of this document may be the subject of
patent rights. ISO shall not be held responsible for identifying any or all such patent rights. Details of
any patent rights identified during the development of the document will be in the Introduction and/or
on the ISO list of patent declarations received (see www.iso.org/patents).
Any trade name used in this document is information given for the convenience of users and does not
constitute an endorsement.
For an explanation of the voluntary nature of standards, the meaning of ISO specific terms and
expressions related to conformity assessment, as well as information about ISO's adherence to the
World Trade Organization (WTO) principles in the Technical Barriers to Trade (TBT), see www.iso.org/
iso/foreword.html.
This document was prepared by Technical Committee ISO/TC 43, Acoustics, Subcommittee SC 1, Noise.
A list of all parts in the ISO 1996 series can be found on the ISO website.
Any feedback or questions on this document should be directed to the user’s national standards body. A
complete listing of these bodies can be found at www.iso.org/members.html.
iv
Introduction
Noise with prominent impulsive sound is more annoying than continuous types of noise (without
impulses or tones) with the same equivalent sound pressure level. Therefore, an adjustment is
commonly added to the measured L , if prominent impulsive sound is present.
Aeq
In ISO 1996, three categories of impulsive sound have been found to correlate best with community
response, and adjustments are given for each. Sources of impulsive sound are listed for each category.
However, the list is not exhaustive.
This method objectively categorises sources by determining the prominence of impulsive sound at
the receiver point, with the aim of correlating to human response. The resulting adjustments can be
used to categorise the sources or be applied directly. It describes specific methodology for this purpose
and provides guidance to cognizant authorities for categorising sources and their adjustments. It is
intended to complement the ISO 1996-2 measurement method for general purpose environmental noise
assessment.
v
PUBLICLY AVAILABLE SPECIFICATION ISO/PAS 1996-3:2022(E)
Acoustics — Description, measurement and assessment of
environmental noise —
Part 3:
Objective method for the measurement of prominence of
impulsive sounds and for adjustment of L
Aeq
1 Scope
This method objectively categorises sources by determination of the prominence of impulsive sound,
with the aim of correlating to community response. This method for measuring the prominence of
impulsive sounds is intended for sources not identified as gunfire or high-energy impulsive sound. It
typically produces adjustments in the range 0,0 dB to 9,0 dB. These adjustments are intended to be
used to categorise the sources as either regular impulsive or highly impulsive sound sources and
apply the penalty indicated in ISO 1996-1. However, the adjustments may be applied directly, as is
[2] [3]
done in NT ACOU 112 , and BS 4142 . ISO 1996-2 provides additional guidance for performing these
measurements.
The method is intended for use on sources with impulsive characteristics that are not already
categorised in ISO 1996-1. A non-exhaustive list of examples includes compressed air release, scrap
handling, goods delivery, fork lifts with rattling forks, skateboard ramps, industrial shearing, gas
discharges, percussive tools in demolition, powered riveting, etc.
The method is not intended for use on sounds from firearms. Although the measurements of prominence
may give relevant results, research has shown the response to these sources is influenced by factors
outside of the scope of this document. In addition, the method is not intended to use for high-energy
impulsive sound sources as specified in ISO 1996-1.
NOTE This method is not intended for occupational hearing loss, which is outside the scope of this document.
See Annex A for recommended additional research.
2 Normative references
The following documents are referred to in the text in such a way that some or all of their content
constitutes requirements of this document. For dated references, only the edition cited applies. For
undated references, the latest edition of the referenced document (including any amendments) applies.
ISO 1996-1, Acoustics — Description, measurement and assessment of environmental noise — Part 1: Basic
quantities and assessment procedures
IEC 61672-1, Electroacoustics — Sound level meters — Part 1: Specifications
3 Terms and definitions
For the purposes of this document, the following terms and definitions apply.
ISO and IEC maintain terminology databases for use in standardization at the following addresses:
— ISO Online browsing platform: available at https:// www .iso .org/ obp
— IEC Electropedia: available at https:// www .electropedia .org/
3.1
sound pressure level
L
pAF
A frequency-weighted and F time-weighted sound pressure level
Note 1 to entry: The sound pressure level is as defined in ISO 1996-1.
3.2
impulsive sound
sound with a sudden onset
Note 1 to entry: The definition includes only the onset of a sound, not the sound as a whole. ”Sudden” is based on
an auditive judgement, which is expressed in terms of physical measurements in this method.
Note 2 to entry: The perceived characteristics and prominence of an impulsive sound at the immission point
depends on the character of the emitted sound, the distance and propagation path from the sound source and
the residual sound. Therefore, the onset parameters characterize the impulse independent of the category of the
sound source.
3.3
onset
contiguous part of the positive slope of the time history of L where the gradient exceeds 10 dB/s
pAF
Note 1 to entry: The starting point of an onset is the point where the gradient first exceeds 10 dB/s. The end
point of an onset is the first point after the starting point where the gradient decreases to less than 10 dB/s.
Irregularities (on the onset) shorter than 50 ms are excluded.
3.4
level difference
LD
difference in decibels of L between the level of the end point L and the level of the starting point L
pAF e s
of the onset (3.3)
3.5
onset rate
OR
slope in decibels per second of the straight line that gives the best approximation to the onset (3.3)
between the starting point and the end point
Note 1 to entry: For pass-bys of, e.g. road vehicles, trains or aircraft the onset rates shall be found from the level
range L − (L − L )/2 to L , i.e. over the upper half of the slope, see Figure 1 illustrating the onset rate (OR)
e e s e
and the level difference (LD) based on the time history of the A frequency-weighted and F time-weighted sound
pressure levels.
Key
LD level difference, in decibels
L level at the starting point, in decibels
s
L level at the end point, in decibels
e
OR onset rate, in decibels per second
t starting point, in seconds
s
t end point, in seconds
e
NOTE Gradients of 10 dB/s or more are indicated with short line segments.
Figure 1 — Analysis of the time history of the A frequency-weighted and F time-weighted sound
pressure levels
3.6
assessment time interval
time interval in which any adjustment is applied
Note 1 to entry: This is typically different than the reference time interval, the measurement time interval and
the observation time interval.
4 Measurements
Measurements shall be made with instruments conforming with Class 1 as specified in IEC 61672-1
with the additional logging of L , the A frequency-weighted and F time-weighted sound pressure level,
pAF
at the intervals identified below.
The A frequency-weighted and F time-weighted sound pressure level shall be sampled with time
intervals in the range 10-25 ms (incl.). Alternatively, measurements made on the basis of short-term
L values (e.g. 10 ms) may be used and, if so, shall (e.g. by computation) be approximated to time
Aeq
weighting F before the readings are taken.
NOTE 1 Direct measurements of L are preferred to those based on short-term L values.
pAF Aeq
NOTE 2 Measurements based on a series of short-term L values can be converted to a series of L values
Aeq pAF
by the following Formula (1):
LL
 pnAF,-1eA q,n  
τ τ
   
 
 
10 10
L =⋅10 lg 1-0⋅+110 // dB (1)
   
pnAF,
  
Δt Δt
   
 
 
  
where
L n’th short-term L value, in decibels;
Aeq,n Aeq
L A frequency-weighted and F time-weighted sound pressure level at the time of the n’th L
pAF,n Aeq
value, L ; L = L , in decibels;
Aeq,n pAF,0 Aeq,0
τ time constant for the time weighting, in ms. For F: τ = 125 ms;
Δt time between the L values (and the integration time), in ms.
Aeq
Measurements based on samples with time intervals of 100 ms may be used for surveys and screening,
as many modern sound level meters ca
...

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ISO/PAS 1996-3:2022는 환경 소음의 기술적 분석을 위한 중요한 기준을 제공합니다. 이 표준은 충격적인 소리의 뚜렷함을 측정하는 객관적인 방법을 제시하여, 지역 사회의 반응과 상관관계를 맺는 데 중점을 두고 있습니다. 이를 통해 소음을 주는 다양한 출처를 효과적으로 분류할 수 있습니다. 특히 이 표준의 강점은 급격한 충격 소리를 높이 에너지를 요구하지 않는 다양한 출처에 적용할 수 있다는 점입니다. 예를 들어, 압축 공기 배출, 쓰레기 처리, 화물 배송 및 산업적인 절단 작업등 다양한 상황에서 이 방법을 사용할 수 있습니다. 이는 ISO 1996-1에서 이미 분류되지 않은 소리의 평가 기준을 제공함으로써 기존의 데이터 세트를 보완하게 됩니다. 조정값은 일반적으로 0.0 dB에서 9.0 dB의 범위 내에서 발생하며, 이는 정기적인 충격 소리와 고충격 소리 출처를 쉽게 구분할 수 있도록 도와줍니다. ISO 1996-2는 이러한 측정 수행에 대한 추가 지침을 제공하여 사용자에게 도움을 줄 수 있습니다. 이 표준은 또한 총상분 리스팅에 대한 제한을 명확히 하여, 특정 출처에 대한 데이터 수집이 필요한 방법론을 제시합니다. 예를 들어, ISO/PAS 1996-3:2022는 총격이나 높은 에너지의 충격 소리 출처에는 적용되지 않는다는 점을 강조합니다. 이는 해당 문서의 범위를 명확히 하고, 소리 측정의 결과가 다른 외부 요인에 의해 왜곡되지 않도록 하는 역할을 합니다. 결과적으로 ISO/PAS 1996-3:2022는 환경 소음 관리와 관련된 연구 및 실무에 있어 중요한 참조 기준이 되며, 다양한 산업 현장에서의 소음 평가에 기여할 수 있는 강력한 도구입니다. 이는 환경 소음의 정량적 측정 및 평가를 보다 체계적이고 신뢰성 있게 만들어, 지역 사회의 소음 문제 해결에 기여할 수 있습니다.

The standard ISO/PAS 1996-3:2022 focuses on the objective method for the measurement of the prominence of impulsive sounds within environmental noise assessments. It serves an essential role in the acoustics field by providing a systematic approach to classify sources of impulsive sounds and evaluate their impact on community response. One notable strength of this standard is its comprehensive framework for categorizing impulsive sound sources that are not classified as gunfire or high-energy impulsive sounds. By establishing a clear method for determining the prominence of these sounds, ISO/PAS 1996-3:2022 allows for more accurate and relevant adjustments in the range of 0.0 dB to 9.0 dB, which can be instrumental in effectively managing noise pollution and its perception within communities. The standard is particularly relevant for a diverse array of sound sources including, but not limited to, compressed air release, goods delivery, and powered riveting. By extending the measurement criteria beyond conventional noise sources, it addresses a gap in existing methodologies, aligning with contemporary challenges in environmental noise management. Furthermore, ISO/PAS 1996-3:2022 recommends utilizing the adjustments in conjunction with the guidelines provided by ISO 1996-1, offering a seamless integration of established standards and new methodologies. The versatility of the method allows it to cater to a range of applications, making it a valuable tool for professionals in acoustics and environmental management. However, it is crucial to note that this standard explicitly excludes high-energy impulsive sounds and firearms, signaling its focused purpose in evaluating less intense impulsive noises. This delineation enhances its specificity and practicality for particular contexts, ensuring that assessments remain relevant and meaningful. Overall, ISO/PAS 1996-3:2022 stands out for its well-defined scope, systematic approach to impulsive sound measurement, and its significant contributions to both community awareness and regulatory compliance in environmental noise assessment. The detailed methodology and its practical applications solidify its importance in contemporary noise management practices.

ISO/PAS 1996-3:2022は、環境ノイズの記述、測定および評価に関する国際基準の一部であり、特に衝撃音の顕著性を測定するための客観的な手法を提供します。この標準の意義は、衝撃音の源を客観的に分類し、地域社会の反応と相関させることにあります。特に、銃声や高エネルギーの衝撃音として特定されていない音源に適用されることを目的としています。 この手法は、0.0 dBから9.0 dBの範囲で調整を提供し、音源を「定期的な衝撃音」または「非常に衝撃的な音源」として分類するためのペナルティを適用することができます。この調整は、ISO 1996-1 に示された基準に基づいて行われます。また、NT ACOU 112やBS 4142のように、調整を直接適用することも可能です。 ISO 1996-2は、測定を行う際の追加的なガイダンスを提供し、ISO 1996-1で分類されていない衝撃的特性を持つ音源についての測定の必要性を強調しています。具体的には、圧縮空気の放出、廃棄物の取り扱い、貨物の配達、騒音を伴うフォークリフト、スケートボードランプ、工業用の剪断、ガス排出、解体作業での振動工具、動力リベットなどが例として挙げられます。 ただし、この手法は銃火器からの音には使用されず、高エネルギー衝撃音源に関してもISO 1996-1で明示されているように適用されません。なお、測定結果が有意義なものである可能性はありますが、反応はこの文書の範囲外の要因にも影響されることが研究によって示されています。この文書は、職業性の聴力損失に関する対応も意図していないため、関連事項に関しては別途附属書Aを参照する必要があります。 このように、ISO/PAS 1996-3:2022は、環境における衝撃音の客観的な分析とその効果的な評価のための重要な手段を提供するものであり、関連するさまざまな状況での適用が期待されます。