Government Decree No. 272 / 2011 Coll.
Government regulation on health protection against adverse effects of noise and vibration
Valid
Regulation
Effective from 01.11.2011
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272
GOVERNMENT REGULATION
of 24 August 2011
on the protection of health from adverse effects of noise and vibration
The Government hereby orders, pursuant to Article 108 (3) of Act No. 258 / 2000 Coll., on the Protection of Public Health and on the amendment of certain related laws, the implementation of Sections 30, 32 and 34 (1) of this Act, as amended, and pursuant to Section 21 (a) of Act No. 309 / 2006 Coll., which regulates further requirements for safety and health at work in employment relations and for the provision of safety and health at work or services outside employment relations (Act on the provision of further conditions for safety and health at work), the implementation of Section 7 (7) of this Act:
SUBJECT MATTER OF THE ADJUSTMENT
This Regulation implements the relevant provisions of the European Union1) and provides for
(a) hygiene limits for noise and vibrations at workplaces, their method of detection and evaluation and the minimum extent of measures to protect the health of workers;
b) sanitary noise limits for protected outdoor space, protected outdoor space of buildings and protected indoor space of buildings,
(c) hygiene limits of vibrations for indoor buildings,
(d) the method of measuring and evaluating noise and vibrations for daytime and night hours.
Basic concepts
For the purposes of this Regulation:
(a) a determining indicator of a physical variable which characterises noise, infrasound, ultrasound or vibration and is used to assess the adverse effects of noise, infrasound, ultrasound and vibration in terms of public health protection;
(b) noise with tone components of noise in whose frequency spectrum the sound pressure level in the third octave band, or even in the two immediately adjacent third octave bands, is more than 5 dB higher than the sound pressure level in the two adjacent third octave bands, and in the 10 Hz to 160 Hz frequency band, the equivalent sound pressure level in that third octave band is higher than the hearing threshold set out for that frequency band in Annex 1 to this Regulation; noise with tone components is always music or singing; if noise with tone components cannot be identified by that definition, a narrowband analysis definition may be used,
(c) high energy impulse noise consisting of sound impulses in the open air, the source of which is explosions in quarries and mines, sonic shocks, demolition and industrial processes with the help of explosives, heavy weapons fire, explosive tests, other sources of explosions whose equivalent mass of trinitrotoluene exceeds 25 g and similar sources, and which meet the criteria set out in Annex 4 to this Regulation in the protected area under consideration;
(d) highly impulsive noise consisting of sound impulses in the outdoor area resulting from light weapons fire, explosions of explosives below 25 g equivalent to the mass of trinitrotoluene and from the impact of solids on each other and which meet the criteria set out in Annex 4 to this Regulation in the protected area under consideration;
(e) variable noise, the sound pressure level of which varies by more than 5 dB at a given location depending on time;
(f) steady-state noise, the sound pressure level of which does not change by more than 5 dB at a given location depending on time;
(g) Lpeak sound pressure level Lpeak the highest instantaneous sound pressure level within a given time interval;
(h) the maximum sound pressure level Lmax the highest sound pressure level within a given time interval;
(i) the permissible exposure limit shall reflect the exposure of the staff member to noise or vibrations converted into an eight-hour shift;
(j) a health limit on exposure to noise or vibration at work for a shift of less than or more than eight hours or as a requirement for work;
(k) the reference period for the assessment of the average noise exposure of weekly, monthly and longer periods within the meaning of the specified standard according to ČSN ISO 1999, which is estimated to be hearing loss due to noise;
(l) the reference period for the assessment of average vibration exposure to weekly, monthly and longer periods within the meaning of the defined standard according to ČSN EN ISO 5349-1, which is measured and evaluated for vibration exposure to hand-transmitted vibration,
(m) the typical flight date of the average operating conditions at the aerodrome derived for the assessment of long-term noise exposure, to be determined as the average 24 hour number of take-offs and landings at the aerodrome, calculated from the total number of take-offs and landings at the aerodrome from 1 May to 31 October of the calendar year; the number of movements shall be separated for daily and nightly periods;
n) railway station sorting station providing train work, train inspection and vehicle repair,
(o) stationary sources of noise, in particular buildings, buildings, premises and premises serving industrial and agricultural production, commercial and administrative activities and services, including transport in these areas, non-moving machinery and equipment fixed in its place or those whose operating radius is restricted at work, portable and ferrous machinery and equipment which do not move as a whole during their use, and marshalling stations; For the purposes of this Regulation, resources related to activities related to the normal use of apartments, houses, family houses, buildings for family recreation and land belonging thereto, with the exception of ventilation and heating facilities, shall not be considered as stationary sources of noise,
(p) maintenance, reconstruction, modernization or optimisation of the track activity related to the replacement or renewal of the rail superstructure, the bottom and related equipment, the panelling and grinding of tracks, possibly the addition of track, pre-electrification, electrification of track or other related modifications;
(q) maintenance, reconstruction, modernisation or capacity building of infrastructure activities related to the laying of a new road surface or road extension, while maintaining the road direction or height line or other related treatment, including a related short-term circumference route;
(r) an area of significant importance for noise penetration of the space prior to the opening of the perimeter of the structure, providing direct natural ventilation in which the protected interior space of the structure is situated, unless this protected space can be directly ventilated otherwise;
s) low-frequency noise in a non-working environment, the most energy of which lies within a frequency band defined by a third octave band with a mean frequency of 10 Hz to 200 Hz;
(t) construction activities activity in the construction site under other legislation4).
_
Constant and variable noise
(1) The permissible exposure limit of steady-state and variable noise at work, expressed in equivalent sound pressure level A LAeq, 8h is 85 dB.
(2) The hygienic limit of steady-state and variable noise for the workplace on which the work of attention and concentration is carried out, as well as for the workplaces intended for creative work, expressed in equivalent sound pressure level A LAeq, 8h is equal to 50 dB.
(3) The hygienic limit of fixed and variable noise for workplaces in production and storage buildings, with the exception of those referred to in paragraph 2, where noise does not arise from work activities carried out at these workplaces but is caused by ventilation or heating equipment of these workplaces, expressed in equivalent sound pressure level A LAeq, T is equal to 70 dB.
(4) The assessment of steady-state and variable noise by average exposure shall be performed when the working time over the reference period is variable or when the noise level changes during the reference period, but the individual daily noise exposure does not differ by more than 10 dB in LAeq, 8h from the results of repeated measurements and at none of the exposures is exceeded by the Lamax 107 dB.
(5) The average noise exposure shall be used instead of the daily noise level to assess the total noise level to which workers are exposed during the period under consideration. The individual daily noise exposure should first be converted into 8 hours working hours.
(6) When determining the average workplace noise exposure over the reference period, the total number of shifts in the period and the number of shifts in which the employee is exposed to noise shall be based.
(7) The procedure referred to in paragraph 5 shall also apply in the case of regular or irregular shifts with a duration of more than 8 hours, at a variable number of hours over the reference period, but the individual daily noise exposure shall first be converted into 8 hours working hours.
(8) The average weekly exposure of LAeq noise, w is calculated according to the relation:
LAeq, w = 10 · lg15,
where n is the number of shifts during weekly working hours during which the staff member is exposed to noise.
(9) The average monthly exposure to LAeq noise, s is calculated according to the relation:
LAeq, s = 10 · lg1s ijk = 1n100,1 · LAeq, 8h, k, dB,
where n is the number of shifts during the monthly working hours in which the staff member is exposed to noise and s is the total number of working days in that month.
(10) The relationship referred to in paragraph 8 shall be treated mutatis mutandis in the calculation of the average exposure of the staff member to noise over the reference period of more than one month.
Impulse noise
(1) The permissible exposure limit for impulse noise, expressed in equivalent sound pressure level A LAeq, 8h is 85 dB.
(2) The permissible exposure limit for impulse noise, expressed as the peak sound pressure level C LCpeak, shall be 140 dB.
(3) The hygiene limit for impulse noise shall apply mutatis mutandis to the workplaces referred to in Article 3 (2) and (3).
(4) The assessment of impulse noise according to the average exposure shall be used when the working time over the reference period is variable or when the noise level changes during the reference period, but the individual daily noise exposure does not differ by more than 10 dB in the equivalent sound pressure level A from the results of repeated measurements and none of the exposures exceed the maximum sound pressure level A Lamax 107 dB.
(5) The calculation of the average weekly exposure to impulse noise shall be determined in accordance with Section 3 (6).
High frequency noise
Allowed exposure limit for high-frequency noise, expressed in equivalent sound level in third octave bands with a mean frequency of 8 kHz, 10 kHz, 12,5 kHz and 16 kHz Lteq, 8h is equal to 75 dB; high-frequency noise is audible sound in a frequency band exceeding 8 kHz.
Ultrasound
Allowed ultrasound exposure limit, expressed in equivalent Lteq sound pressure level, 8h in a third octave band of 20 kHz, 25 kHz, 31,5 kHz and 40 kHz Lteq, 8h is equal to 105 dB.
Infrastics and low frequency noise
(1) The permissible exposure limit for infrasound and low-frequency noise, expressed in equivalent sound pressure level G LGeq, 8h is equal to 116 dB.
(2) The permissible exposure limit of the infrasound, expressed in equivalent sound pressure levels in third octave bands with a mean frequency of 1 Hz to 16 Hz Lteq, 8h is equal to 110 dB.
(3) Allowed low-frequency noise exposure limit, expressed in equivalent sound pressure levels in third octave bands 20 Hz to 40 Hz Lteq, 8h is equal to 105 dB.
(4) For short-term exposure to low-frequency noise within 8 minutes expressed in maximum sound pressure levels of Ltmax in third octave bands with a mean frequency of 1 Hz to 16 Hz, it shall not exceed 137 dB and in third octave bands with a mean frequency of 20 Hz to 40 Hz Ltmax shall not exceed 132 dB.
Hygienic noise, infrasound and ultrasound limit at workplaces other than an eight-hour shift
Hygienic limit of noise exposure, infrasound, low-frequency and high-frequency noise and ultrasound expressed as sound level And for a non-eight-hour shift in minutes, it shall be determined by adding to the permitted exposure limits LAeq, 8h, Lteq, 8h or LGeq, 8h the KT correction to be determined according to the relationship
KT = 10.lg (480 / T), [dB],
where T is different from an eight-hour shift in minutes.
Assessment of noise risk and minimum scope of measures to protect workers' health
(1) In assessing the risk of noise, the employer shall take particular account of:
(a) the level, type and duration of the exposure, including the exposure to impulse noise;
(b) permissible exposure and hygiene limits;
(c) the effects of noise on the health and safety of workers, in particular young workers, pregnant women, breast-feeding women and mothers by the end of the ninth month after birth;
(d) effects on the health and safety of workers resulting from the current exposure to factors forming part of the technology which may thereby increase the risk of injury, in particular hearing,
(e) indirect effects resulting from interactions between noise and warning signals or other sounds to be monitored to reduce the risk of accidents;
(f) information on noise emissions provided by the manufacturer of the machine, tool or other device;
(g) the existence of alternative work equipment designed to reduce noise emissions provided for by other legislation3);
(h) the extension of the noise exposure period over the eight-hour shift;
(i) relevant information resulting from health surveillance and available published information;
(j) the availability of hearing protectors with appropriate attenuation characteristics.
(2) The organisation of the workplace on which the work associated with the exposure to noise, the location of production equipment and equipment, the choice of working tools, working procedures and methods of work is or will be carried out shall aim at reducing the risk of noise at its source.
(3) Training of staff performing work associated with an exposure to steady-state or variable noise whose equivalent sound pressure level A LAeq, 8h exceeds 80 dB, or work associated with exposure to other types of noise whose values exceed their permissible exposure limit shall include in particular information on:
(a) the correct use of means of production, equipment and work tools;
(b) noise sources at the workplace;
(c) the type and effects of the noise and its permissible exposure limits;
(d) results of noise measurement;
(e) measures taken to limit the level and duration of noise exposure;
(f) the correct use of personal protective equipment;
(g) appropriate working procedures to minimise exposure to noise;
(h) procedures for detecting possible hearing damage;
(i) the purpose of medical preventive examinations provided by the provider of occupational medical services.
(4) Noise protection or noise protection systems shall be located in such a way as to absorb such noise or reduce the spread of noise outside such workplaces.
(5) Regular and proper maintenance of production equipment, equipment and work tools at workplaces where noise exposure work is carried out must ensure that the wear and tear rate is not the cause of the noise increase.
(6) A safety break applies when the work is carried out in a noise exposure exceeding the permissible exposure limit. The first break of at least 15 minutes shall be included no later than 2 hours after the start of work. Subsequent breaks of at least 10 minutes shall be included no later than 2 hours after the end of the previous break. The last break of at least 10 minutes shall be included no later than 1 hour before the end of the shift. For safety breaks, the staff member shall not be exposed to noise exceeding the permissible exposure limit.
Minimum range of measures to reduce noise exposure
(1) If the assessment of the measured values shows that, despite the measures applied to eliminate or minimise noise, the equivalent noise levels exceed A permitted exposure limit of 80 dB for an eight-hour shift shall be provided by the employer to staff members with personal protective equipment to protect hearing effective in the area of noise frequencies.
(2) If the permissible exposure limit of 85 dB is exceeded, the employer must ensure that personal protective equipment is used by workers.
NOISE IN THE PROTECTED INTERNAL PROCESSES, IN THE PROTECTED RURAL PROCESSES AND PROTECTED RURAL AREA
Hygienic noise limits in protected indoor spaces of buildings
(1) The sound level A LAeq, T and the maximum sound level A Lamax are equivalent to the noise level A LAeq, T or corresponding levels in the frequency bands. The equivalent sound pressure level A LAeq, T is set for 8 continuous and consecutive noise-related hours (LAeq, 8h) at night for the loudest 1 hour (LAeq, 1h). For road and rail noise and air traffic noise, the equivalent sound pressure level A LAeq, T shall be determined for the whole day (LAeq, 16h) and the whole night (LAeq, 8h). In the case of air traffic noise, the hygiene limit in the protected indoor areas of the buildings applies to a typical flight day.
(2) Hygienic limit of equivalent sound level A shall be determined for ambient air noise and for building noise within the object by the sum of the basic sound pressure level A LAeq, T shall be equal to 40 dB and the corrections taking into account the type of protected space and the daytime and night time referred to in Annex 2 to this Regulation. In the case of noise with tone components, except noise from road, rail and air traffic, additional correction -5 dB shall be added.
(3) Hygienic limit of equivalent sound level A from air traffic refers to a characteristic flight day and is determined for the whole day by the sound pressure level A LAeq, 16h is equal to 40 dB and for the whole night by the sound pressure level A LAeq, 8h is equal to 30 dB.
(4) Hygienic limit of maximum sound level A shall be determined for noise spreading from sources within the object by adding the basic maximum sound pressure level A Lamax equal to 40 dB and corrections taking into account the type of protected interior space and the daytime and night time referred to in Annex 2 to this Regulation. In the case of noise with tone components, except noise from road, rail and air traffic, additional correction -5 dB shall be added. Noise from sources inside the building, with the exception of noise from construction activity, is also considered to be noise from sources located outside this building, which penetrates this building in a way other than air, in particular by constructions or subsoil.
(5) Hygienic limit of equivalent sound level For noise from the construction activity inside the LAeq object, s is determined by adding + 15 dB to the sanitary limit equivalent to the sound pressure level A LAeq, T determined in accordance with paragraph 2 in working days for the period between the seventh and twenty-first hours of correction.
(6) Hygienic limit of equivalent sound level And for the sound of electronically amplified music, the audience space is determined for the time T is equal to 4 hours Laeq, T is equal to 100 dB.
Hygienic noise limits in protected outdoor areas of buildings and in protected outdoor areas
(1) The indicative noise indicator, except for high energy impulse noise, is the equivalent sound pressure level A LAeq, T and the corresponding levels in the frequency bands. During the day it is set for 8 continuous and consecutive loudest hours (LAeq, 8h), at night for the loudest 1 hour (LAeq, 1h). For road and rail noise and air traffic noise, the equivalent sound pressure level A LAeq, T shall be determined for the whole day (LAeq, 16h) and the whole night (LAeq, 8h).
(2) The indicator of high energy impulse noise is equivalent to the sound pressure level C LCeq, T and the mean sound exposure level C LCE of individual impulses. It is set for 8 continuous and consecutive hours (LCeq, 8h), at night for the loudest 1 hour (LCeq, 1h).
(3) The hygiene limit of the equivalent sound pressure level A, with the exception of air traffic noise and high energy impulse noise, is determined by the sum of the basic sound pressure level A Laeq, T 50 dB and the corrections taking into account the type of protected space and the daytime and night hours listed in Table 1 of Part A of Annex 3 to this Regulation. For high impulse noise, additional correction -12 dB is added. In the case of noise with tone components, except noise from road, rail and air traffic, additional correction -5 dB shall be added.
(4) The hygienic limit of equivalent sound level C of high energy impulse noise is determined for the daily LCeq time, 8h is equal to 83 dB, for the night LCeq time, 1h is equal to 40 dB. The equivalent sound pressure level C LCeq, T shall be calculated in accordance with Part C of Annex 3 to this Regulation.
(5) Hygienic limit of equivalent sound level A from air traffic refers to a characteristic flight day and is determined for the whole day by the sound pressure level A LAeq, 16h is equal to 60 dB and for the whole night by the sound pressure level A LAeq, 8h is equal to 50 dB.
(6) Hygienic limit of equivalent sound level A for noise from construction activity LAeq, s shall be determined by adding further corrections to the hygiene limit equivalent to the sound pressure level A LAeq, T as determined in accordance with paragraph 3 of Part B of Annex 3 to this Regulation.
VIBRATION ON WORKERS
Allowed vibration exposure limit
(1) Allowed exposure limit of hand-transmitted vibration expressed as an average aggregate weighted
(a) the level of acceleration of vibrations of the Lahv, 8h equals 128 dB; or
b) value of acceleration of vibration ahv, 8h is equal to 2,5 m.s.2
(2) For vibrations transmitted on the hands of workers, the permissible exposure limit refers to the aggregate value of translational vibrations determined from weighted acceleration values in three perpendicular directions according to the hand coordinate system.
(3) Allowed vibration exposure limit transmitted in a special way to workers causing intensive oscillation at the upper spine and head expressed as an average weighted
(a) the Law vibration acceleration level, 8h is equal to 100 dB; or
b) value of aew vibration acceleration, 8h is equal to 0,1 m.s.2
(4) Allowed exposure limit of total vertical and horizontal vibrations transmitted to staff expressed as an average weighted
(a) the Law vibration acceleration level, 8h in dB is equal to 114 dB; or
b) value of aew vibration acceleration, 8h is equal to 0,5 m.s-2.
(5) The permissible exposure limit for total vibrations applies to both fixed and variable vibrations and shocks or shocks when the main part of their energy is contained in the monitored frequency band.
(6) Total vibrations parallel to the longitudinal axis of the body are assessed in a manner applicable to vertical vibrations and vibrations in directions perpendicular to the longitudinal axis of the body in a manner applicable to horizontal vibrations.
Hygienic vibration limit for non-eight-hour shift
(1) The hygiene limit of the average aggregate weighted vibration acceleration levels for a non-eight-hour shift in minutes shall be determined by adding to the permissible exposure limit Law, 8h or Lahw, 8h the KT correction to be determined according to the relationship
KT = 10.lg480 / T, dB.
(2) The hygiene limit of the average weighted vibration acceleration values for a non-eight-hour shift in minutes is determined by multiplying the permissible exposure limit aew, 8h or ahv by the kT factor determined by the relationship
kT = 480T, -,
(3) The KT correction and the kT factor for a non-eight-hour shift are not used for the assessment of vibration transmitted in a special way.
(4) For exposure to total vibrations over 10 minutes and less, the hygiene limit shall be 131 dB or 3,55 m.s.2
(5) For hand-transmitted vibration exposure for 20 minutes and shorter, the hygiene limit is 142 dB or 12,5 m.s-2.
Average exposure
(1) The vibration assessment according to the average exposure shall be performed when the working time is variable over the reference period or when the vibration changes during the reference period, but the individual daily vibration exposure does not differ by more than 10 dB in Lawi or by a multiple of 3 in aewi from the results of repeated measurements and at none of them the permissible exposure limit or, where appropriate, the permitted exposure limit adjusted by the KT correction or by the kT factor.
(2) In order to assess the overall level of vibration to which workers are exposed during activity, where vibration exposure varies significantly between daily vibration exposures during the reference period, the average vibration exposure shall be used instead of the daily level of vibration acceleration or vibration acceleration. Individual daily vibration exposure should first be converted into 8 hours of working time. For individual vibration sources measured, frequency analysis shall be performed. If the dominant components of the frequency weighted acceleration are at lower frequencies, conversion to the reference period cannot be applied.
(3) In determining the average exposure to vibrations at the workplace over the reference period, the total number of shifts in the period and the number of shifts in which the employee is exposed to vibrations is based.
(4) The procedure referred to in paragraph 2 shall also apply in the case of regular or irregular shifts with a duration of more than 8 hours, with a variable number of hours over the reference period, but the individual daily vibration exposure shall first be converted into 8 hours working hours.
(5) The average weekly vibration exposure expressed by the mean aggregate weighted acceleration level of Law, w shall be calculated according to the relation:
Law, w = 10 · lg15 vijk = 1n100,1 · Law, 8h, k, dB,
where n is the number of shifts during weekly working hours in which the employee is exposed to vibration.
(6) The average weekly vibration exposure expressed by the average aggregated weighted effective value of the aew vibration acceleration, w is calculated according to the relation:
aew, w = 15 dost ri = 1naew, 8h, i2, m.s-2,
where n is the number of shifts during weekly working hours in which the employee is exposed to vibration.
(7) The average monthly vibration exposure expressed by the mean aggregate weighted acceleration level of LAW shall be determined according to the relation:
Law, s = 10 · lg1s vizk = 1n100,1 · Law, 8h, k, dB,
where n is the number of shifts during the monthly working hours in which the employee is exposed to vibration and s is the total number of working days in that month.
(8) The average monthly vibration exposure expressed by the average aggregated effective value of the aew vibration acceleration shall be determined according to the relation:
aew, s = 1s, i = 1naew, 8h, i2, m.s-2,
where n is the number of shifts during the monthly working hours in which the employee is exposed to vibration and s is the total number of working days in that month.
(9) According to the relationship referred to in paragraph 7, the average exposure of an employee to vibration over the reference period shall be treated mutatis mutandis for more than one month.
Hygienic limits for total vertical vibrations of less than 0,5 Hz
(1) Hygienic limit of the average weighted acceleration of total vertical vibrations with a frequency below 0,5 Hz
(a) for an exposure period not exceeding 120 min Law, T is equal to 120 dB or aew, T is equal to 1 m.s-2; and
(b) for an exposure period exceeding 120 min Law, T is equal to 114 dB or aew, T is equal to 0,5 m.s-2.
(2) Hygienic limits for total vertical vibrations of less than 0,5 Hz refer to working positions on self-driving machines and their time of exposure to workers.
Assessment of vibration risk and health protection measures
(1) The employer shall carry out a risk assessment based on the knowledge of the data on the estimated level of vibration load and conditions of use of the equipment indicated by the manufacturer. The assessment of the risk on the basis of the knowledge of the data reported by the manufacturer shall not replace measurements. The assessment and measurement of vibrations shall be carried out regularly and further whenever conditions of work change.
(2) In assessing the risk of vibration, the employer shall take particular account of:
(a) the type and duration of exposure, including exposure to intermittent vibration and repeated shocks;
(b) permissible exposure or hygiene limits laid down for the types of vibration concerned;
(c) the effects of vibration on the health and safety of young workers, pregnant women, breast-feeding women and mothers by the end of the ninth month after birth;
(d) indirect effects on the safety of the worker resulting from interactions between vibration and the work site or other equipment;
(e) the creation of conditions to ensure safe work and safe workplaces using information provided by manufacturers of work equipment;
(f) the possibility of introducing technical equipment designed to reduce vibration exposure;
(g) extension of exposure to total vibrations over eight-hour working hours;
(h) working conditions associated with vibration exposure, in particular cold loads;
(i) relevant information resulting from health surveillance and available published information.
(3) Where an employee is exposed at work to vibrations exceeding the exposure limit or the hygiene limit referred to in § 14 (1) or (2), it shall apply mutatis mutandis to the inclusion of security breaks during the shift. During the security break, the staff member shall not be exposed to vibrations exceeding the permissible exposure or hygiene limit.
VIBRATION IN PROTECTED INTERNAL PROCESSES AND WORKERS
(1) Hygienic vibration limit in protected building space expressed as an average weighted
(a) the LAW vibration acceleration level, T is equal to 75 dB; or
(b) the aew acceleration value, T is equal to 0,0056 m / s2.
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Regulation Information
| Citation | Government Decree No. 272 / 2011 Coll., on the protection of health against adverse effects of noise and vibration |
|---|---|
| Regulation Type | Regulation |
| Author | - |
| Collection | Code of Laws |
| Date of Promulgation | 23.09.2011 |
|---|---|
| Effective from | 01.11.2011 |
| Effective until | - |
| Status | Valid |
The regulation text is for informational purposes only.
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