Technical Report: What is a sound level meter?
13. Laws regarding noise.
About the Noise Regulation Law
The regulation on noise generated by industrial activities and the permissible limits for automobile noise was promulgated on June 10, 1968, and came into effect on December 1 of the same year.
Article 1 states that the purpose of this law is "to regulate the considerable range of noise generated by business activities in factories and workplaces, as well as construction work, and to establish permissible limits for automobile noise, thereby preserving the living environment and contributing to the protection of public health." It regulates "specific factories and related regulations," "regulations concerning specific construction work," and "permissible limits for automobile noise, etc."
"The 'Permissible Limits for Automobile Noise' refers to the 'permissible limits for the magnitude of automobile noise' and includes an order that establishes limits for automobile noise within designated areas. These regulations were revised and came into effect on April 1, 2000. Below is an excerpt from the noise regulation law for your reference. For more details, please refer to this law and related local ordinances established based on it."
Standards regarding the regulation of noise generated in specific factories and similar places.
Table 13-7 "Noise Generated in Specific Factories and Similar Environments"
| division of areas | division of time | Remarks | ||
| daytime | morning and evening | nighttime | ||
| (7 AM, 8 AM ~ 6 PM, 7 PM, 8 PM) |
(5, 6 to 7, 8 AM) (6, 7, 8 to 9, 10, 11 PM) |
(9, 10, 11 PM - 5, 6 AM the next day) |
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| (Type 1 Area) To preserve a good residential environment, areas that particularly require the maintenance of tranquility. |
below 45 to 50 dB | below 40 to 45 dB | 40 to 45 dB |
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| (Category 2 Area) Designated for residential use, requiring the maintenance of tranquility in the area. |
50 to 60 | 45 to 50 | 40 to 50 | |
| (Type 3 Zone) A zone that is provided for residential use along with commercial and industrial uses, and it is necessary to prevent noise generation in order to preserve the living environment of the residents in that zone. |
60 to 65 | 55 to 65 | 50 to 55 | |
| (Type 4 Area) An area primarily used for industrial purposes, where it is necessary to prevent significant noise generation in order to avoid deteriorating the living environment of the residents within that area. |
65 to 70 | 60 to 70 | 55 to 65 | |
Standards Regarding the Regulation of Noise Generated During Specific Construction Activities
Table 13-8 "Noise Generated During Specific Construction Activities"
|
types of work |
regulatory standards | condition |
Remarks |
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|---|---|---|---|---|---|---|---|
| Nighttime or late-night work |
daily working hours | work period | Sunday Sunday, and other holidays |
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| 1. Work using a pile driver, pile extractor, or pile driving and extraction machine. | Excluding the use of the monken. Excluding the press-in type pile driving and pile extraction machines. Excluding the operation that shares the pile driver with the earth auger. | below 85 dB | Prohibited in area ① from 7 AM to 7 AM the next day, and in area ② from 10 PM to 6 AM the next day. | Area 1: 10 hours, Area 2: 14 hours | Consecutive 6 days in the same place. | prohibit |
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| 2. Work using a nail gun. | |||||||
| 3. Work using a rock drill. | In work where the work site moves continuously, it is limited to work where the maximum distance between two locations in one day does not exceed 50 meters. | ||||||
| 4. Work using an air compressor. | Only power sources other than electric motors with a rated output of 15 kW or more are permitted, excluding work using rock drilling machines. | ||||||
| 5. Work carried out by establishing a concrete plant or asphalt plant. | Only those with a kneading capacity of 0.45 m 3 or more for the kneader are allowed. Only those with a kneading weight of 200 kg or more for the kneader are allowed. Excluding work done by setting up a concrete plant to produce mortar. |
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(3) Permissible limits related to automobile noise
The reference value changed from L 50 to L Aeq on April 1, 2000.
Table 13-9 Request limit values related to automobile noise
(Cabinet Order establishing limits for automobile noise in designated areas)
|
division of areas |
division of time | ||||||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| daytime | nighttime | ||||||||||||||
| 1 | an area facing a road with one lane in either area a or area b | 65 dB | 55 dB | ||||||||||||
| 2 | an area facing a road with two or more lanes | 70 dB | 65 dB | ||||||||||||
| 3 | Area b, which faces a road with two or more lanes, and area c, which faces a road with lanes. |
75 dB | 70 dB | ||||||||||||
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In the areas listed in the above table, the limits concerning areas adjacent to roads that carry main traffic (for roads with two lanes or fewer, this refers to a range of 15 meters from the boundary of the road property; for roads with more than two lanes, it refers to a range of 20 meters from the boundary of the road property) shall be set at 75 dB during the day and 70 dB at night, regardless of the above table. |
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Method for measuring automobile noise.
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Noise measurements should be conducted at the boundary line of the road property when there are residences, hospitals, schools, or similar facilities adjacent to the road. If the residences are located at a distance from the road, measurements should be taken at a point where the noise level can be accurately assessed at the residences. The height at which measurements are taken should be at the position where noise is most problematic for the preservation of the living environment in the vertical direction. Intersections should be avoided.
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The measurement will evaluate the equivalent noise level based on 3 days recognized as representative of the automobile noise situation during a continuous 7-day period. The magnitude of the noise will be determined by averaging the measured values over the entire time period, based on the principle of 3 days.
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Noise measurement shall be conducted using a sound level meter that meets the conditions of Article 71 of the Measurement Law, and measurements shall be taken at a position that avoids the influence of reflections from buildings, according to the measurement methods specified in JIS Z 8731. If it is not possible to avoid such influences, the measured values shall be adjusted accordingly. If there are influences from noise other than automobile noise, these influences shall also be considered when adjusting the measured values.
Permissible limits of automobile noise levels
The "Permissible Limits for Automobile Noise Levels (Notification by the Environmental Agency)" based on the Noise Regulation Act was revised in February 2000, resulting in a reduction of 1 dB to 3 dB for acceleration noise, 1 dB to 6.1 dB for steady-state noise, and 5 dB to 8 dB for close exhaust noise compared to previous values. Additionally, the methods for measuring noise for vehicles subject to strengthened regulations have also been changed. For details, see Table 13-10.
Table 13-10 Permissible Limit Values for Automobile Noise Levels (Ministry of the Environment Notification, 2000)
|
types of automobiles |
the permissible limit of automobile noise volume |
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|---|---|---|---|---|---|
| steady driving noise | close exhaust noise | acceleration driving noise | |||
| Ordinary cars, small cars, and light vehicles (excluding passenger vehicles designed primarily for use with a seating capacity of ten or fewer and motorcycles). | Vehicles with a total weight exceeding 3.5 tons and a maximum engine output exceeding 150 kW. | A vehicle equipped with a power transmission device that can transmit power to all wheels, used for towing semi-trailers and for crane operations. | 83 dB | 99 dB | 82 dB |
| A vehicle equipped with a power transmission device that can transmit power to all wheels, excluding those used for towing semi-trailers and those used for crane operations. | 82 dB | 99 dB | 81 dB | ||
| Vehicles with a total weight exceeding 3.5 tons and a maximum engine output of 150 kW or less. | A power transmission device equipped with a structure that can transmit power to all wheels. | 80 dB | 98 dB | 81 dB | |
| anything other than those equipped with a power transmission device that can transmit power to all wheels. | 79 dB | 98 dB | 80 dB | ||
| vehicles with a total weight of 3.5 tons or less | 74 dB | 97 dB | 76 dB | ||
| Ordinary automobiles, small cars, and light vehicles (excluding motorcycles) that are primarily used for passenger transport and have a seating capacity of ten or fewer. | those having an engine at the rear of the vehicle. | 72 dB | 100 dB | 76 dB | |
| Things other than those having an engine at the rear of the vehicle. | 72 dB | 96 dB | 76 dB | ||
| Small motor vehicle (limited to two-wheeled vehicles.) | 72 dB | 94 dB | 73 dB | ||
| Light motor vehicle (limited to motorcycles). | 71 dB | 94 dB | 73 dB | ||
| Type 1 motorized bicycle (referring to the Type 1 motorized bicycle as defined in Article 1, Section 2 of the regulations; the same applies hereafter.) | 65 dB | 84 dB | 71 dB | ||
| Type 2 motorized bicycle (referring to the Type 2 motorized bicycle as defined in Article 1, Section 2 of the regulations; the same applies hereafter.) | 68 dB | 90 dB | 71 dB | ||
Overview of the Environmental Impact Assessment Act
The Environmental Impact Assessment Law, based on the Basic Environmental Law, recognizes the critical importance of conducting environmental impact assessments in advance by businesses undertaking projects such as land alteration and the establishment of new facilities, clarifying the responsibilities of the state and others. It establishes procedures to ensure that environmental impact assessments are conducted appropriately and smoothly, and aims to reflect the results of these assessments in project content, taking measures to ensure proper consideration for environmental conservation. The ultimate goal is to contribute to securing the health and cultural living standards of current and future citizens. This law was enacted in June 1999. Environmental assessment was institutionalized in the United States in 1969, and in response to the increasing global environmental pollution issues, many countries are advancing the legislation of similar laws.
What is an environmental impact assessment?
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Conduct investigations, predictions, and evaluations regarding the environmental impact of the project in advance, by examining each component of the environment (scoping).
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During the execution of the project, measures and considerations will be taken to ensure that environmental conservation related to the project is maintained.
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Comprehensive evaluation of environmental impacts after implementation and in the case where those measures have been taken.
It refers to actions that are carried out within the internal operations of a business.
Screening and Scoping
It stipulates a system for selecting projects that are large in scale and may have significant environmental impacts, which the government must implement or authorize, mandating that environmental impact assessments be conducted for projects above a certain scale ("Type 1 projects"). It also defines projects that have a scale similar to Type 1 projects ("Type 2 projects") and discusses the necessity of conducting environmental impact assessments based on the differences in each project and region.
Type 1 projects include the construction and improvement of expressways, general national roads, and large-scale forest roads; the construction of power generation facilities and dams, as well as the construction and improvement of weirs; the construction and improvement of railways and airports; the establishment or modification of final disposal sites for general and industrial waste; land reclamation and drainage projects; land readjustment; the development of industrial parks; new residential urban development; new urban infrastructure development; and the development of distribution business parks.
In conducting an environmental impact assessment, it is stipulated to determine effective survey items and methods for advancing the evaluation (scoping). The business plan will be advertised and opinions from residents will be widely accepted. Our company has prepared environmental noise prediction software "SoundPLAN" for noise.
Figure 13-1
Summary of Noise Evaluation Metrics in Japan's Environmental Noise Measurement
Table 13-10 Summary of Noise Evaluation Metrics in Japan's Environmental Noise Measurement
| Type | evaluation metric | law | Citation of JIS Z 8731 |
|---|---|---|---|
| road traffic noise | Equivalent noise level LAeq | Basic Environmental Law | new |
| Railway (Shinkansen) noise | LA (Slow) peak value power average | old | |
| railway (conventional line) noise | Find LAeq from LAE | ||
| aircraft noise | WECPNL LA(Slow) | ||
| Aircraft noise (effective April 2013) | Lden (equivalent continuous noise level adjusted for time of day) | new | |
| Noise from factories, business establishments, and construction sites | For steady noise, the indicated value LA (Slow) | Noise Regulation Law | old |
| For fluctuating noise: upper limit value of 90% range (L5) < LA (Fast) to be determined > |
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In the case of intermittent noise:
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| automobile traffic noise | Equivalent noise level LAeq | new | |
| automobile standalone noise | LA (Fast) | ||
| Work environment noise | LAeq (Slow) equivalent noise level for 10 minutes | Labor Safety and Health Regulations | old |
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