GOST 12.1 014 84 indicator tubes. Method for measuring concentrations of harmful substances with indicator tubes

STATE STANDARD OF THE UNION OF THE SSR

Occupational safety standards system

Air working area

Method for measuring concentrations harmful substances
indicator tubes

GOST 12.1.014-84

MOSCOW

APPROVED AND INTRODUCED BY Decree of the USSR State Committee for Standards dated December 14, 1984 No. 4362

INSTEAD OF GOST 12.1.014-79

The validity period was removed by decision of the Interstate Council for Standardization, Metrology and Certification (Minutes No. 5-94)

REPUBLICATION (January 1996) with Amendment No. 1 approved in March 1990 (IUS 7-90)

This International Standard establishes an accelerated method for measuring concentrations of harmful substances in the air of a working area with indicator tubes, except for the air of underground mine workings.

The essence of the method is to change the color of the indicator powder as a result of a reaction with a harmful substance (gas or steam) in the analyzed air sucked through the tube. The concentration of a harmful substance is measured by the length of the layer of indicator powder in the tube that has changed its initial color (linear-color indicator tube) or by its intensity (colorimetric indicator tube).

The terms used in the standard and their explanations are given in the appendix.

Characteristics of the produced indicator powders are given in the appendix.

The normalized metrological characteristics of indicator tubes and air intake devices for them are given in the appendix.

STATE STANDARD OF THE UNION OF THE SSR

Occupational safety standards system

Working area air

Method for measuring concentrations of harmful substances

indicatortubes

Occupational safety standards system.
Air of the work zone. Method of measuring unhealthy matters
concentration using indicator tubes

GOST
12.1.014-84

Instead
GOST 12.1.014-79

Introduction date 1986-01-01

1. EQUIPMENT

1.1. Indicator tubes, including those supplied by the consumer using special sets with indicator powders.

1.2. Filter tubes, including those supplied by the consumer using special kits.

1.3. An air intake device (such as a pump, bellows, etc.) designed for use with this indicator tube.

2. PREPARATION FOR MEASUREMENT

2.1. Preparation of equipment for measuring concentrations of harmful substances in the air of the working area is carried out in accordance with regulatory documentation on the indicator and filter tubes and the air intake device intended for them.

2.2. In unexplored production conditions, before carrying out measurements with indicator tubes, it is necessary to conduct a one-time qualitative assessment of the composition of the air in the working area using certified methods or guidelines approved by the Ministry of Health of the USSR. Based on the data obtained, the possibility of using indicator tubes for planned or operational control is established. Regardless of the composition of the air in the working area, the use of filter tubes with indicator tubes, if it is provided for in the regulatory documentation for indicator tubes, is mandatory in order to avoid violating the operating conditions of indicator tubes.

A repeated qualitative assessment of the composition of the air in the working area should be carried out with each change in production technology, which can cause the appearance of new harmful substances in the air.

2.1, 2.2 (Revised edition, Rev. No. 1).

3. MEASURING

barometric pressure - from 90 to 104 kPa (680-780 mm Hg);

relative humidity - 30 - 80%;

temperature - from 288 to 303 K.

Deviation from the specified parameters is allowed, if it is provided for in the regulatory and technical documentation for measuring instruments.

Control of the metrological parameters of the air in the working area should be carried out in parallel with measurements of the concentrations of harmful substances with indicator tubes.

3.2. An indicator tube is attached to the air intake device, designed to measure the concentration of a harmful substance, and filter tubes, if they are provided for by regulatory documentation.

The measurement should be started no later than 1 min after the depressurization of the tubes.

3.1, 3.2 (Revised edition, Rev. No. 1).

3.3. The amount of air sucked through the indicator tubes is set in accordance with the regulatory documentation for these tubes.

concentration ( With n) under normal conditions in mg / m 3 is calculated by the formula

where is the result of measuring the concentration of a harmful substance, at ambient temperature, t°С, relative humidity φ % and atmospheric pressure R kPa, mg/m 3 ;

K AT - coefficient taking into account the influence of temperature and humidity of the surrounding air on the readings of indicator tubes, the value of which is determined in accordance with paragraph of the appendix.

The relative measurement error (δ) should not exceed ±35% in the range up to 2.0 maximum allowable concentrations (MPC) inclusive and ±25% at concentrations above 2.0 MPC under the conditions specified in paragraph .

The measurement result is presented as: ( With H ± Δ) mg / m 3 with a confidence level of 0.95.

The value of the absolute errorDcalculated according to the formula

In the range up to 1.0 MPC, the error may increase up to ±60%. This value of the relative error must be indicated in the regulatory and technical documentation for measuring instruments.

(Revised edition, Rev. No. 1).

4. SAFETY REQUIREMENTS

4.1. When measuring the concentration of harmful substances with indicator tubes in the air of the working area, the safety standards and rules in force in this production should be observed.

4.2. Measurement of the concentration of harmful substances with indicator tubes is carried out by persons who have been trained and admitted to work on the control of harmful substances in the air of the working area.

4.3. When opening the tubes, all safety precautions when working with glass must be observed, using special devices and means of protection.

APPLICATION 1
Reference

TERMS USED IN THE STANDARD AND THEIR EXPLANATIONS

Explanation

Work zone

Method for measuring the concentration of harmful substances

According to GOST 16263-70

harmful substance

Maximum permissible concentrations of harmful substances in the air of the working area

indicator tube

Primary measuring transducer, structurally representing a glass tube filled with granular filler (indicator powder)

Linear color indicator tube

An indicator tube that allows you to measure the concentration of a harmful substance in the analyzed air sucked through the tube along the length of the indicator powder layer in the tube that has changed its initial color

Colorimetric indicator tube

An indicator tube that makes it possible to judge the presence of a harmful substance in the analyzed air sucked through the tube at a concentration higher than the triggering concentration for this indicator tube by the color intensity of the indicator powder by comparing it with a control sample of the indicator effect

filter tube

A glass tube filled with one or more absorbers used to trap gases and vapors that interfere with the measurement of a harmful substance

indicator powder

A granular chemisorbent that changes color when a directly detectable harmful substance or its volatile products of interaction with a chemisorbent in a filter tube passes through it

Absorber

A granular sorbent or chemisorbent that completely passes the harmful substance to be determined and captures related substances that interfere with the analysis

Indication range

Range of values ​​of the scale of the indicator tube, limited by the final and initial values ​​of the scale

Lower (upper) limit

The smallest (greatest) value of the measured concentrations

Air intake device

Device for sucking air through indicator tubes

(Revised edition, Rev. No. 1).

APPLICATION 2
Reference

CHARACTERISTICS OF PRODUCED INDICATOR POWDERS FOR EQUIPMENT OF INDICATOR TUBES

Detected gas (steam)

Sucked air volume, cm 3

Measurement range, mg/m 3

Total air suction time, s

Gas (steam) captured by the filter cartridge

Gas (steam) interfering with the determination

nitrogen oxides

Halogens (chlorine, bromine, iodine), ozone in concentrations above 10 MPC

Pairs of acids, alkalis and amines

Sulfurous anhydride

Hydrogen sulfide, ammonia, nitrogen dioxide, sulfuric acid mist, water vapor

Acetylene

Hydrogen sulfide, hydrogen phosphide, silicic hydrogen, ammonia, acetone and water vapours.

Sulfurous anhydride, vapors of acetic acid, acetic anhydride, hydrochloric acid, in concentrations up to 10 MPC

Pairs of ketones and esters, vapors of acetic acid, acetic anhydride, hydrochloric acid and sulfurous anhydride in concentrations above 10 MPC

Aromatic and unsaturated hydrocarbons, water vapor

400´ 3

360´ 3

water vapor

water vapor

Pairs of fatty and aromatic hydrocarbons

hydrogen sulfide

Mercaptans

water vapor

Pairs of fatty and aromatic hydrocarbons

Petroleum hydrocarbons

Unsaturated and aromatic hydrocarbons, water vapor

Carbon oxide

Acetylene, ethylene, methane, a mixture of butane and propane, nitrogen oxides, chlorine, sulfur dioxide, hydrogen, gasoline vapors, benzene and its homologues, water, acetone, formic acid, formaldehyde, ethyl and methyl alcohols, dichloroethane, carbon disulfide

Pairs of metal carbonyls

Vapors of bromine, iodine, oxidizing agents, chloramines

Ethyl ether

Vapors of water, ethyl alcohol, organic acids, phenol

(Revised edition, Rev. No. 1).

APPLICATION 3
Reference

RATED METROLOGICAL CHARACTERISTICS OF INDICATOR PIPES AND AIR INTAKE DEVICES TO THEM

1. Metrological characteristics

1.1. For linear-color indicator tubes, the following metrological characteristics are established:

nominal static conversion characteristic,

range of measured concentrations,

basic error,

relative error,

influence functions caused by a change in the influence quantity within operating conditions.

1.2. The characteristics of indicator tubes designed to determine the presence of a harmful substance in the air of the working area (colorimetric indicator tubes) are:

the nominal value of the concentration of a harmful substance that causes the appearance of an indication effect (trigger concentration);

operation error.

1.3. For air intake devices, the following metrological characteristics are established:

the amount of air sucked in,

error in dosing the volume of sucked-in air.

Instead of volume, it is allowed to normalize the duration of suction and the volume flow of air sucked through the indicator tube.

2. Methods of normalization and forms of presentation of metrological characteristics

2.1. The nominal static conversion characteristic is presented in the form of a formula or graph, which corresponds to the scale printed on the indicator tube, cassette or special label.

2.2. The range of measured concentrations is characterized by its lower and upper limits. The lower limit of the measurement range should be no more than 0.5 of the maximum allowable concentration, and the upper limit - at least 5 maximum allowable concentrations for a given substance.

It is allowed to divide the measurement range into several sub-ranges by changing the volume of air sucked through the indicator tube, setting the nominal value for each of these volumes. static characteristic transformations.

If the range of indications does not coincide with the measurement range, then the range of indications is normalized by setting the initial and final values ​​of the scale.

2.3. The basic error of the indicator tubes is characterized by the limit of the permissible basic error. The values ​​​​of the limit of permissible basic error must be selected from the series established in GOST 8.401-80.

At the development stages of indicator tubes, their main error is characterized by:

the limit of the permissible value of the systematic component of the basic error,

limit of the permissible value of the average standard deviation random component of the basic error.

2.4. The number of successively used indicator tubes, which ensures the reduction of the error in the result of measuring the concentration of a harmful substance to values ​​not exceeding those specified in clause of this standard, is established in the regulatory documentation and should not exceed 5.

2.8. The regulatory documentation for specific indicator tubes includes data on impurities in the gas-air environment that interfere with the measurement of the concentration of this harmful substance. An impurity is considered non-interfering if, at an impurity concentration at a level of 5 maximum permissible values ​​for it, the value of the basic error of the indicator tube is less than the established limit.

2.9. The regulatory documentation for indicator tubes must specify the storage conditions and the warranty period of storage, during which the error values ​​of the indicator tubes are within the established limits.

The values ​​of the warranty period of storage of indicator tubes are selected from row 1; 1.5; 2; 3 and 5 years old.

2.10. The volume of air sucked through the indicator tube by means of an air intake device is expressed in cm 3 .

The error in dosing the volume of sucked-in air is characterized by the limit of the permissible value and is selected from a range of 5, 3, 2, 1 and 0.5%.

An air sampling device intended for use with an indicator tube must have the same flow characteristics as the air sampling device used for calibrating the indicator tube.

Name:

System of labor safety standards. Work area air. Method for measuring concentrations of harmful substances with indicator tubes

Active

Introduction date:

Cancellation date:

Replaced with:

Text GOST 12.1.014-84 Occupational safety standards system. Work area air. Method for measuring concentrations of harmful substances with indicator tubes

GOST 12.1.014-84

INTERSTATE STANDARD

SYSTEM OF WORK SAFETY STANDARDS

AIR of the working area

METHOD FOR MEASURING CONCENTRATIONS OF HARMFUL SUBSTANCES

INDICATOR PIPES

Official edition

Standartinform

UDC 614.71:543.27:006.354

Group T58

INTERSTATE STANDARD

Occupational safety standards system

WORK AREA AIR

Method for measuring concentrations of harmful substances with indicator tubes

Occupational safety standards system. GOST 12.1.014-79

Air in the zone of operation. Method of measuring unhealthy matters concentration using indicator tubes

MKC 13.040.30 OKSTU 0012

Decree of the USSR State Committee for Standards of December 14, 1984 No. 4362 established the introduction date

01.01.86

The validity period was removed according to protocol No. 5-94 of the Interstate Council for Standardization, Metrology and Certification (IUS 11-12-94)

This International Standard establishes an accelerated method for measuring concentrations of harmful substances in the air of a working area with indicator tubes, except for the air of underground mine workings.

The essence of the method is to change the color of the indicator powder as a result of a reaction with a harmful substance (gas or steam) in the analyzed air sucked through the tube. The concentration of a harmful substance is measured by the length of the layer of indicator powder in the tube that has changed its initial color (linear-color indicator tube) or by its intensity (colorimetric indicator tube).

The terms used in the standard and their explanations are given in Appendix 1.

Characteristics of the produced indicator powders are given in Appendix 2.

Standardized metrological characteristics of indicator tubes and air intake devices for them are given in Appendix 3.

1. EQUIPMENT

1.1. Indicator tubes, including those supplied by the consumer using special sets with indicator powders.

1.2. Filter tubes, including those supplied by the consumer using special kits.

1.3. An air intake device (such as a pump, bellows, etc.) designed for use with this indicator tube.

2. PREPARATION FOR MEASUREMENT

2.1. Preparation of equipment for measuring the concentration of harmful substances in the air of the working area is carried out in accordance with the regulatory and technical documentation for indicator and filter tubes and the air intake device intended for them.

2.2. In unexplored production conditions, before taking measurements with indicator tubes, it is necessary to conduct a one-time qualitative assessment of the composition of the air in the working area using certified methods or guidelines approved by the USSR Ministry of Health. Based on the data obtained, the possibility

Official publication Reprint prohibited

Edition (October 2010) with Revision No. 1 approved March 1990

© Standards Publishing House, 1984 © Standartinform, 2010

the use of indicator tubes for planned or operational control. Regardless of the composition of the air in the working area, the use of filter tubes with indicator tubes, if it is provided for in the regulatory and technical documentation for indicator tubes, is mandatory in order to avoid violating the operating conditions of indicator tubes.

A repeated qualitative assessment of the composition of the air in the working area should be carried out with each change in production technology, which can cause the appearance of new harmful substances in the air.

2.1, 2.2. (Revised edition, Rev. No. 1).

3. MEASURING

3.1. Measurement of concentrations of harmful substances in the air of the working area is carried out with the following parameters:

barometric pressure - from 90 to 104 kPa (680-780 mm Hg);

relative humidity - 30-80%;

temperature - from 288 to 303 K.

Deviation from the specified parameters is allowed, if it is provided for in the regulatory and technical documentation for measuring instruments.

The control of meteorological parameters of the air in the working area should be carried out in parallel with the measurements of the concentrations of harmful substances with indicator tubes.

3.2. An indicator tube is attached to the air intake device, designed to measure the concentration of a harmful substance, and filter tubes, if they are provided for by regulatory and technical documentation.

The measurement should be started no later than 1 min after the depressurization of the tubes.

3.1, 3.2. (Revised edition, Rev. No. 1).

3.3. The amount of air sucked through the indicator tubes is set in accordance with the normative and technical documentation for these tubes.

3.4. Measurement of concentrations of harmful substances is carried out sequentially under production conditions in accordance with GOST 12.1.005-88. In this case, the number of indicator tubes specified in the relevant regulatory and technical documentation is used.

3.5. The concentration of a harmful substance in mg / m 3 in the air of the working area is measured by the length or intensity of the indicator powder layer that has changed its initial color using a scale printed on the indicator tube, cassette or special label. The measurement result is taken as the arithmetic mean of successive observations, as indicated in paragraph 3.4.

3.6. When the interface between the colors of the layers of the initial and reacted indicator powder is blurred, the concentration of the measured harmful substance on the scale is measured along the lower and upper parts of the boundary. The average value is taken as the measurement result.

3.7. The result of measuring the concentration of a harmful substance is brought to normal conditions (C n): temperature 293 K, atmospheric pressure 101.3 kPa (760 mm Hg), relative humidity 60%.

The concentration (C n) under normal conditions in mg / m 3 is calculated by the formula

C n C|,f, r

(273 + 0-101.3 293 r

where C v f,/; - the result of measuring the concentration of a harmful substance, at ambient temperature t ° C, relative humidity f % and atmospheric pressure p kPa, mg / m 3;

K in - coefficient taking into account the influence of ambient temperature and humidity on the readings of indicator tubes, the value of which is determined in accordance with paragraph 2.5 of Appendix 3.

The relative measurement error (b) should not exceed +35% in the range up to 2.0 maximum allowable concentrations (MPC) inclusive and +25% at concentrations above 2.0 MPC under the conditions specified in clause 3.1.

The measurement result is presented as: (C n + A) mg/m 3 with a confidence level of 0.95.

The absolute error (A) is calculated by the formula

In the range up to 1.0 MAC, inclusive, an increase in the error up to + 60% is allowed. This value of the relative error must be indicated in the regulatory and technical documentation for measuring instruments.

(Revised edition, Rev. No. 1).

4. SAFETY REQUIREMENTS

4.1. When measuring the concentration of harmful substances with indicator tubes in the air of the working area, the safety standards and rules in force in this production should be observed.

4.2. Measurement of the concentration of harmful substances with indicator tubes is carried out by persons who have been trained and admitted to work on the control of harmful substances in the air of the working area.

4.3. When opening the tubes, it is necessary to observe all safety precautions when working with glass, using special devices and protective equipment.

APPENDIX 1 Reference

TERMS USED IN THE STANDARD AND THEIR EXPLANATIONS

Work zone

Method for measuring the concentration of harmful substances Harmful substance Maximum permissible

concentration of harmful substances in the air of the working area

According to GOST 12.1.005-88 According to RMG 29-99

According to GOST 12.1.007-76 According to GOST 12.1.005-88

Explanation

indicator tube

Linear color tube

Primary measuring transducer, structurally representing a glass tube filled with granular filler (indicator powder)

An indicator tube that allows you to measure the concentration of a harmful substance in the analyzed air sucked through the tube along the length of the indicator powder layer in the tube that has changed its initial color

Colorimetric indicator tube

An indicator tube that makes it possible to judge the presence of a harmful substance in the analyzed air sucked through the tube at a concentration higher than the triggering concentration for this indicator tube by the color intensity of the indicator powder by comparing it with a control sample of the indicator effect

filter tube

A glass tube filled with one or more absorbers used to trap gases and vapors that interfere with the measurement of a harmful substance

indicator powder

A granular chemisorbent that changes color when a directly detectable harmful substance or its volatile products of interaction with a chemisorbent in a filter tube passes through it

Absorber

A granular sorbent or chemisorbent that completely passes the harmful substance to be determined and captures related substances that interfere with the analysis

Indication range

Range of values ​​of the scale of the indicator tube, limited by the final and initial values ​​of the scale

Lower (upper) limit Air intake device

The lowest (highest) value of measured concentrations Device for sucking air through indicator tubes

APPENDIX 2 Reference

CHARACTERISTICS OF PRODUCED INDICATOR POWDERS FOR EQUIPMENT OF INDICATOR TUBES

Detected gas (steam)

Sucked air volume, cm 3

Range

measurement,

Total air suction time, s

Gas (steam) captured by the filter cartridge

Gas (steam) interfering with the determination

nitrogen oxides

Halogens (chlorine, bromine, iodine), ozone in concentrations above 10 MPC

Pairs of acids, alkalis

Serum anhydride

hydrogen sulfide, ammonia,

nitrogen dioxide, sulfuric acid mist, water vapor

Acetylene

Hydrogen sulfide, phospho-

Hydrogen hydrate, silicic hydrogen, ammonia, acetone and water vapours.

Sulfurous anhydride,

Pairs of ketones and complex

vapors of acetic acid,

ethers, a pair of vinegar-

acetic anhydride, salt-

noic acid, acetic

noic acid in concentrated

anhydride, hydrochloric acid

up to 10 MPC

lots and anhydride series-

in concentrations above 10 MPC

Aromatic and unsaturated hydrocarbons, water vapor

water vapor

Vapors of hydrocarbons

water vapor

Vapors of hydrocarbons

fatty and aromatic series

hydrogen sulfide

Mercaptans

water vapor

Vapors of hydrocarbons

fatty and aromatic series

hydrocarbons

Hydrocarbons

sensible and aromatic, water vapor

Carbon ok-

Acetylene, ethylene, methane,

Pairs of carbonyls me-

mixture of butane and propane,

nitrogen oxides, chlorine, sulfurous anhydride, hydrogen, vapors of gasoline, benzene and

its homologues, water, acetone, formic acid, formaldehyde, ethyl and methyl alcohols, dichloroethane, carbon disulfide

Vapors of bromine, iodine, oxidizing agents, chloramines

Ethyl

Vapors of water, ethyl

alcohol, organic acids, phenol

APPENDICES 1, 2. (Changed edition, Amendment No. 1).

APPENDIX 3

Mandatory

RATED METROLOGICAL CHARACTERISTICS OF INDICATOR PIPES AND AIR INTAKE DEVICES TO THEM

1. Metrological characteristics

1.1. For linear-color indicator tubes, the following metrological characteristics are established:

nominal static conversion characteristic, range of measured concentrations, basic error, relative error,

influence functions caused by a change in the influence quantity within operating conditions.

1.2. The characteristics of indicator tubes designed to determine the presence of a harmful substance in the air of the working area (colorimetric indicator tubes) are:

the nominal value of the concentration of a harmful substance that causes the appearance of an indication effect (trigger concentration); operation error.

1.3. For air intake devices, the following metrological characteristics are established: the volume of air sucked in,

error in dosing the volume of sucked-in air.

Instead of volume, it is allowed to normalize the duration of suction and the volume flow of air sucked through the indicator tube.

2. Methods of normalization and forms of presentation of metrological characteristics

2.1. The nominal static conversion characteristic is presented in the form of a formula or graph, which corresponds to the scale printed on the indicator tube, cassette or special label.

2.2. The range of measured concentrations is characterized by its lower and upper limits. The lower limit of the measurement range should be no more than 0.5 of the maximum allowable concentration, and the upper limit - at least 5 maximum allowable concentrations for a given substance.

It is allowed to divide the measurement range into several sub-ranges by changing the volume of air sucked through the indicator tube, setting the nominal static conversion characteristic for each of these volumes.

If the range of indications does not coincide with the measurement range, then the range of indications is normalized by setting the initial and final values ​​of the scale.

2.3. The basic error of the indicator tubes is characterized by the limit of the permissible basic error. The values ​​of the limit of permissible basic error must be selected from the series established in GOST 8.401-80.

At the stages of development of indicator tubes, their main error is characterized by: the limit of the permissible value of the systematic component of the main error, the limit of the permissible value of the standard deviation of the random component of the main error.

2.4. The number of successively used indicator tubes, which ensures the reduction of the error in the result of measuring the concentration of a harmful substance to values ​​not exceeding those specified in and. 3.7 of this standard, set in the regulatory and technical documentation and should be no more than 5.

2.5. The influence function is normalized in the form of a graph or table and takes into account the effect on the readings of the indicator tube of joint changes in temperature and relative humidity of the ambient air within the conditions specified in and. 3.1 of this standard.

The influence function is not normalized if the additional error is within the conditions specified in and. 3.1 of this standard does not exceed 20% of the maximum permissible basic error.

2.6. The nominal value of the concentration of a harmful substance that causes the appearance of an indication effect in colorimetric indicator tubes (trigger concentration) is expressed in mg/m 3 .

2.7. The error of the colorimetric indicator tube is characterized by the limit of the permissible relative error of the response concentration. The values ​​of the limit of permissible basic error must be selected from the series established in GOST 8.401-80.

2.8. The regulatory and technical documentation for specific indicator tubes includes data on impurities in the gas-air environment that interfere with the measurement of the concentration of this harmful substance. An impurity is considered non-interfering if, at an impurity concentration at a level of 5 maximum permissible values ​​for it, the value of the basic error of the indicator tube is less than the established limit.

2.9. The regulatory and technical documentation for the indicator tubes must specify the storage conditions and the guaranteed storage period, during which the error values ​​of the indicator tubes are within the established limits.

The values ​​of the warranty period of storage of indicator tubes are selected from row 1; 1.5; 2; 3 and 5 years old.

2.10. The volume of air sucked through the indicator tube by means of an air intake device is expressed in cm 3 .

The error in dosing the volume of sucked-in air is characterized by the limit of the permissible value and is selected from a range of 5, 3, 2, 1 and 0.5%.

An air sampling device intended for use with an indicator tube must have the same flow characteristics as the air sampling device used for calibrating the indicator tube.

Editor M.I. Maksimova Technical editor N.S. Grishanova Proofreader V.E. Nesterova Computer layout L.A. Circular

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  • GOST R ISO 16000-13-2012 Air of enclosed spaces. Part 13: Determination of the total content of polychlorinated dioxin-like biphenyls (PCBs) and polychlorinated dibenzo-paradioxins/dibenzo-furans (PCDD/PCDF) (in gaseous state and in the form of suspended solids). Sampling for filter and sorbent
  • GOST R ISO 16000-14-2013 Air of enclosed spaces. Part 14: Determination of the total content of polychlorinated dioxin-like biphenyls (PCBs) and polychlorinated dibenzo-para-dioxins/dibenzo-furans (PCDD/PCDF) (in gaseous state and in the form of suspended solids). Extraction, purification and analysis by gas chromatography and high-resolution mass spectrometry
  • GOST R ISO 16000-15-2012 Air of enclosed spaces. Part 15: Sampling for nitrogen dioxide (NO2) determination
  • GOST R ISO 16000-17-2012 Air of enclosed spaces. Part 17. Detection and enumeration of molds. Cultivation Method
  • GOST R ISO 16000-18-2013 Air of enclosed spaces. Part 18. Detection and enumeration of molds. Sampling by sedimentation
  • GOST R ISO 16000-25-2013 Air of enclosed spaces. Part 25. Determination of emissions of medium volatile organic compounds from building materials. Micro camera method
  • GOST R ISO 16183-2013 Highly loaded engines. Measurement of gaseous emissions in undiluted exhaust gases and particulate emissions using a partial flow dilution system in fast-changing tests
  • GOST R ISO 17736-2013 Working area air. Determination of isocyanates in air using a dual filter sampler and high performance liquid chromatography
  • GOST R ISO 21438-2-2012 Working area air. Determination of inorganic acids by ion chromatography. Part 2: Volatile acids other than hydrofluoric (hydrochloric, hydrobromic and nitric acids)
  • GOST R ISO 21438-3-2012 Working area air. Determination of inorganic acids by ion chromatography. Part 3: Hydrofluoric acid and solid fluorides
  • GOST 32531-2013 Benzidine. Measurement of benzidine concentration in water using liquid-liquid extraction or solid-phase extraction and reverse-phase high-performance liquid chromatography/particle beam interface/mass spectrometry
  • GOST R 56640-2015 Clean rooms. Design and installation. General requirements
  • GOST R ISO 14382-2015 Working area air. Determination of toluene diisocyanate vapors using glass fiber filters impregnated with 1-(2-pyridyl)-piperazine and analysis by high performance liquid chromatography with ultraviolet and fluorescent detectors
  • GOST R ISO 16000-26-2015 Air of enclosed spaces. Part 26: Sampling for determination of carbon dioxide (CO2) content
  • GOST R ISO 28439-2015 Working area air. Characteristics of ultrafine aerosols and nanoaerosols. Determination of particle size distribution and number concentration of particles using differential electrical mobility analysis systems
  • GOST 32596-2013 Benzidine. Measurement of the concentration of benzidine in water by gas chromatography - mass spectrometry
  • GOST R 55175-2012 Mine atmosphere. Dust Control Methods
  • GOST R 56638-2015 Clean rooms. Ventilation and air conditioning. General requirements
  • GOST R ISO 16000-28-2015 Air of enclosed spaces. Part 28: Determination of odor emissions from building materials using test chambers
  • GOST 31824-2012 Fibrous mist eliminators. Types and basic parameters. Safety requirements. Test Methods
  • GOST 31830-2012 Electrostatic precipitators. Safety requirements and test methods
  • GOST 31831-2012 Centrifugal dust collectors. Safety requirements and test methods
  • GOST R 54578-2011 Working area air. Aerosols are predominantly fibrogenic. General principles for hygiene control and exposure assessment
  • GOST R 54597-2011 Working area air. Ultrafine aerosols, aerosols of nanoparticles and nanostructured particles. Characterization and inhalation exposure assessment
  • GOST R ISO 11614-2011 Compression ignition piston internal combustion engines. A device for measuring smoke and determining the coefficient of absorption of light flux in exhaust gases
  • GOST R ISO 16000-12-2011 Air of enclosed spaces. Part 12: Sampling of polychlorinated biphenyls (PCBs), polychlorinated dibenzo-para-dioxins (PCDDs), polychlorinated dibenzofurans (PCDFs) and polycyclic aromatic hydrocarbons (PAHs)
  • GOST R ISO 16000-7-2011 Air of enclosed spaces. Part 7: Sampling for determination of asbestos fiber content
  • GOST R ISO 16000-8-2011 Air of enclosed spaces. Part 8. Determining the local average "age" of air in buildings to assess ventilation conditions
  • GOST R ISO 16362-2009 Atmospheric air. Determination of the content of polycyclic aromatic hydrocarbons in the form of solid particles by high performance liquid chromatography
  • GOST R ISO 21438-1-2011 Working area air. Determination of inorganic acids by ion chromatography. Part 1. Non-volatile acids (sulfuric and phosphoric)
  • GOST R ISO 14644-6-2010 Clean rooms and associated controlled environments. Part 6. Terms
  • GOST 33554-2015 Automobile vehicles. The content of pollutants in the air of the driver's cabin and the passenger room. Technical requirements and test methods
  • GOST 33670-2015 Single motor vehicles. Examination and test methods for conformity assessment
  • GOST R 53562-2009 Working area air. Basic provisions for the choice of sampling and analysis methods for the content of isocyanates in the air
  • GOST R ISO 12884-2007 Atmospheric air. Determination of the total content of polycyclic aromatic hydrocarbons (in the gaseous state and in the form of suspended solids). Sampling for the filter and sorbent with subsequent analysis by chromato-mass spectrometry
  • GOST R ISO 14644-3-2007 Clean rooms and associated controlled environments. Part 3. Test methods
  • GOST R ISO 14644-7-2007 Clean rooms and associated controlled environments. Part 7: Isolation devices (clean air shelters, glove boxes, isolators and mini-environments)
  • GOST R ISO 14965-2008 Air quality. Determination of non-methane organic compounds. Method of preliminary cryogenic concentration and direct determination using a flame ionization detector
  • GOST R ISO 15202-3-2008 Working area air. Determination of metals and metalloids in solid aerosol particles by inductively coupled plasma atomic emission spectrometry. Part 3. Analysis
  • GOST R ISO 16000-1-2007 Air of enclosed spaces. Part 1. Sampling. General provisions
  • GOST R ISO 16000-10-2009 Air of enclosed spaces. Part 10. Determination of the emission of volatile organic compounds from building and finishing materials. Test cell method
  • GOST R ISO 16000-11-2009 Air of enclosed spaces. Part 11. Determination of the emission of volatile organic compounds from building and finishing materials. Selection, storage and preparation of samples for testing
  • GOST R ISO 16000-3-2007 Indoor air. Part 3. Determination of the content of formaldehyde and other carbonyl compounds. Active sampling method
  • GOST R ISO 16000-5-2009 Air of enclosed spaces. Part 5: Sampling of volatile organic compounds (VOCs)
  • GOST R ISO 16000-6-2007 Indoor air. Part 6. Determination of volatiles organic compounds in the air of enclosed spaces and the test chamber by active sampling for Tenax TA sorbent followed by thermal desorption and gas chromatographic analysis using MSD/FID
  • GOST R ISO 16000-9-2009 Air of enclosed spaces. Part 9. Determination of the emission of volatile organic compounds from building and finishing materials. Test chamber method
  • GOST R ISO 16017-2-2007 Atmospheric air, working area and enclosed spaces. Sampling of volatile organic compounds using a sorption tube followed by thermal desorption and gas chromatographic analysis on capillary columns. Part 2: Diffusion sampling method
  • GOST R ISO 16107-2009 Working area air. Performance evaluation of diffusion samplers
  • GOST R ISO 16200-1-2007 Work area air quality. Sampling of volatile organic compounds followed by solvent desorption and gas chromatographic analysis. Part 1. Sampling by pumping method
  • GOST R ISO 16200-2-2007 Work area air quality. Sampling of volatile organic compounds followed by solvent desorption and gas chromatographic analysis. Part 2: Diffusion sampling method
  • GOST R ISO 16702-2008 Work area air quality. Determination of the total content of isocyanate groups of organic compounds in the air by liquid chromatography using 1-(2-methoxy-phenyl) piperazine
  • GOST R ISO 17734-1-2009 Analysis of organonitrogen compounds in air by liquid chromatography and mass spectrometry. Part 1. Determination of isocyanates by their dibutylamine derivatives
  • GOST R ISO 17734-2-2009 Analysis of organonitrogen compounds in air by liquid chromatography and mass spectrometry. Part 2. Determination of amines and aminoisocyanates by their dibutylamine and ethyl chloroformate derivatives
  • GOST R ISO 8178-5-2009 Reciprocating internal combustion engines. Measurement of emissions of harmful substances. Part 5. Fuels for testing
  • GOST R ISO 9359-2007 Air quality. Stratified sampling method for air quality assessment
  • GOST R 57256-2016 Air of enclosed spaces. Sampling in the determination of ammonia
  • GOST R ISO 11771-2016 Air quality. Determination of time-averaged mass emissions and emission factors. General Approach
  • GOST R ISO 13137-2016 Working area air. Pumps for individual sampling of chemical and biological substances. Requirements and test methods
  • GOST R ISO 17091-2016 Working area air. Determination of the content of lithium hydroxide, sodium hydroxide, potassium hydroxide and calcium dihydroxide. Method based on the measurement of the respective cations by ion suppression chromatography
  • GOST ISO 16000-21-2016 Indoor air. Part 21. Detection and enumeration of molds. Material sampling
  • GOST ISO 16000-3-2016 Indoor air. Part 3. Determination of formaldehyde and other carbonyl compounds in indoor air and in test chamber air. Active sampling method
  • GOST ISO 16000-4-2016 Indoor air. Part 4. Determination of formaldehyde. Diffusion sampling method
  • GOST ISO 16000-6-2016 Indoor air. Part 6: Determination of volatile organic compounds in indoor and test chamber air by active sampling for Tenax TA sorbent followed by thermal desorption and gas chromatography analysis using MSD/FID
  • GOST R 57669-2017 Working area air. Devices for sampling bioaerosol volumetric samples. Requirements and test methods
  • GOST R ISO 12219-5-2017 Air of the internal space of motor vehicles. Part 5: Screening for VOC emissions from interior trim and interior materials. Static method using a test chamber
  • GOST R ISO 16258-1-2017 Working area air. Analysis of inhaled crystalline silicon by X-ray diffraction. Part 1. Method of direct measurement using a filter
  • GOST R ISO 17734-1-2017 Analysis of organonitrogen compounds in air by liquid chromatography and mass spectrometry. Part 1. Determination of isocyanates by their dibutylamine derivatives
  • GOST R ISO 17734-2-2017 Analysis of organonitrogen compounds in air by liquid chromatography and mass spectrometry. Part 2. Determination of amines and aminoisocyanates by their dibutylamine and ethyl chloroformate derivatives
  • GOST R ISO 30011-2017 Working area air. Determination of the content of metals and metalloids in solid aerosol particles by inductively coupled plasma mass spectrometry
  • GOST R ISO 14644-1-2017 Clean rooms and associated controlled environments. Part 1. Classification of air purity by particle concentration
  • GOST R ISO 8178-5-2017 Reciprocating internal combustion engines. Measurement of emissions of combustion products. Part 5. Fuel for testing
  • GOST ISO 16000-20-2017 Indoor air. Part 20. Detection and enumeration of molds. Determination of the total number of disputes
  • GOST ISO 16000-27-2017 Indoor air. Part 27: Determination of the presence of settled fibrous dust on surfaces using SEM (Scanning Electron Microscope) (direct method)
  • GOST ISO 16000-29-2017 Indoor air. Part 29: Test methods for VOC detectors
  • GOST ISO 16000-30-2017 Indoor air. Part 30. Organoleptic analysis of indoor air
  • GOST ISO 16000-32-2017 Indoor air. Part 32. Evaluation of buildings for the presence of pollutants
  • GOST ISO 14644-1-2002 Clean rooms and associated controlled environments. Part 1. Classification of air purity
  • GOST ISO 14698-1-2005 Clean rooms and associated controlled environments. Biocontamination control. Part 1. General principles and methods
  • GOST ISO 14698-2-2005 Clean rooms and associated controlled environments. Biocontamination control. Part 2. Analysis of data on biocontaminants
  • GOST R EN 13205-2010 Working area air. Evaluation of the performance of instruments for the determination of particulate matter
  • GOST R EN 13528-1-2010 Atmospheric air quality. Diffusion samplers used in the determination of the content of gases and vapors. Requirements and test methods. Part 1. General requirements
  • GOST R EN 13528-2-2010 Atmospheric air quality. Diffusion samplers used in the determination of the content of gases and vapors. Requirements and test methods. Part 2: Special requirements and test methods
  • GOST R EN 13528-3-2010 Atmospheric air quality. Diffusion samplers used in the determination of the content of gases and vapors. Requirements and test methods. Part 3. Selection, use and maintenance guide
  • GOST R EN 1822-2-2012 EPA, HEPA and ULPA high-performance air purification filters. Part 2: Aerosol generation, test equipment, particle counting statistics
  • GOST R EN 1822-3-2012 EPA, HEPA and ULPA high-performance air purification filters. Part 3: Flat filter material tests
  • GOST R EN 1822-4-2012 EPA, HEPA and ULPA high-performance air purification filters. Part 4: Filter Leakage Tests (Scan Method)
  • GOST R EN 1822-5-2014 EPA, HEPA and ULPA high-performance air purification filters. Part 5. Determining the efficiency of filter elements
  • GOST R EN 482-2012 Working area air. General requirements for the characteristics of methods for measuring the content of chemicals

Working area air

Method for measuring concentrations of harmful substances

indicator tubes

GOST 12.1.014-84

STATE STANDARD OF THE UNION OF THE SSR

Occupational safety standards system

Working area air

Method for measuring concentrations of harmful substances GOST

indicator tubes 12.1.014-84

Occupational safety standards system. Air of Instead

the work zone. Method of measuring GOST 12.1.014-79

unhealthy matters concentration using

Introduction date 1986-01-01

APPROVED AND INTRODUCED BY Decree of the USSR State Committee for Standards dated December 14, 1984 No. 4362

INSTEAD OF GOST 12.1.014-79

The validity period was removed by decision of the Interstate Council for Standardization, Metrology and Certification (Minutes No. 5-94)

REPUBLICATION (January 1996) with Amendment No. 1 approved in March 1990 (IUS 7-90)

This International Standard establishes an accelerated method for measuring concentrations of harmful substances in the air of a working area with indicator tubes, except for the air of underground mine workings.

The essence of the method is to change the color of the indicator powder as a result of a reaction with a harmful substance (gas or steam) in the analyzed air sucked through the tube. The concentration of a harmful substance is measured by the length of the layer of indicator powder in the tube that has changed its initial color (linear-color indicator tube) or by its intensity (colorimetric indicator tube).

The terms used in the standard and their explanations are given in Appendix 1.

Characteristics of the produced indicator powders are given in Appendix 2.

Standardized metrological characteristics of indicator tubes and air intake devices for them are given in Appendix 3.

1. Hardware

1.1. Indicator tubes, including those supplied by the consumer using special sets with indicator powders.

1.2. Filter tubes, including those supplied by the consumer using special kits.

1.3. An air intake device (such as a pump, bellows, etc.) designed for use with this indicator tube.

2. Preparation for measurement

2.1. Preparation of equipment for measuring the concentration of harmful substances in the air of the working area is carried out in accordance with the regulatory documentation for indicator and filter tubes and the air intake device intended for them.

2.2. In unexplored production conditions, before taking measurements with indicator tubes, it is necessary to conduct a one-time qualitative assessment of the composition of the air in the working area using certified methods or guidelines approved by the USSR Ministry of Health. Based on the data obtained, the possibility of using indicator tubes for planned or operational control is established. Regardless of the composition of the air in the working area, the use of filter tubes with indicator tubes, if it is provided for in the regulatory documentation for indicator tubes, is mandatory in order to avoid violating the operating conditions of indicator tubes.

A repeated qualitative assessment of the composition of the air in the working area should be carried out with each change in production technology, which can cause the appearance of new harmful substances in the air.

2.1, 2.2 (Revised edition, Rev. No. 1).

3. Taking a measurement

3.1. Measurement of concentrations of harmful substances in the air of the working area is carried out with the following parameters:

barometric pressure - from 90 to 104 kPa (680-780 mm Hg);

relative humidity - 30-80%;

temperature - from 288 to 303 K.

Deviation from the specified parameters is allowed, if it is provided for in the regulatory and technical documentation for measuring instruments.

Control of the metrological parameters of the air in the working area should be carried out in parallel with measurements of the concentrations of harmful substances with indicator tubes.

3.2. An indicator tube is attached to the air intake device, designed to measure the concentration of a harmful substance, and filter tubes, if they are provided for by regulatory documentation.

The measurement should be started no later than 1 min after the depressurization of the tubes.

3.1, 3.2 (Revised edition, Rev. No. 1).

3.3. The amount of air sucked through the indicator tubes is set in accordance with the regulatory documentation for these tubes.

3.4. Measurement of concentrations of harmful substances is carried out sequentially under production conditions in accordance with GOST 12.1.005-88. In this case, the number of indicator tubes specified in the relevant regulatory documentation is used.

3.5. The concentration of a harmful substance in mg / m 3 in the air of the working area is measured by the length or intensity of the indicator powder layer that has changed its initial color using a scale printed on the indicator tube, cassette or special label. The measurement result is taken as the arithmetic mean of successive observations as specified in 3.4.

3.6. When the interface between the colors of the layers of the initial and reacted indicator powder is blurred, the concentration of the measured harmful substance on the scale is measured along the lower and upper parts of the boundary. The average value is taken as the measurement result.

3.7 The result of measuring the concentration of a harmful substance is brought to normal conditions ( C n): temperature 293 K, atmospheric pressure 101.3 kPa (760 mm Hg), relative humidity 60%.

concentration ( C n) under normal conditions in mg / m 3 is calculated by the formula

where is the result of measuring the concentration of a harmful substance, at ambient temperature, t°С, relative humidity

- % and atmospheric pressure kPa, mg/m 3 ;

Coefficient that takes into account the effect of ambient temperature and humidity on the readings of indicator tubes, the value of which is determined in accordance with paragraph 2.5 of Appendix 3.

The relative measurement error should not exceed ± 35% in the range up to 2.0 maximum allowable concentrations (MPC) inclusive and ± 25% at concentrations above 2.0 MPC under the conditions specified in clause 3.1.

The measurement result is presented as: mg/m 3 with a confidence level of 0.95.

The value of the absolute error D calculated according to the formula

In the range up to and including 1.0 MPC, an increase in the error up to ± 60% is allowed. This value of the relative error must be indicated in the regulatory and technical documentation for measuring instruments.

(Revised edition, Rev. No. 1).

4. Safety requirements

4.1. When measuring the concentration of harmful substances with indicator tubes in the air of the working area, the safety standards and rules in force in this production should be observed.

4.2. Measurement of the concentration of harmful substances with indicator tubes is carried out by persons who have been trained and admitted to work on the control of harmful substances in the air of the working area.

4.3. When opening the tubes, it is necessary to observe all safety precautions when working with glass, using special devices and protective equipment.

Appendix 1
(reference)

Terms used in the standard and their explanations

Term

Explanation

Work zone

According to GOST 12.1.005-88

Method for measuring the concentration of harmful substances

According to GOST 16263-70

harmful substance

According to GOST 12.1.007-76

Maximum permissible concentrations of harmful substances in the air of the working area

According to GOST 12.1.005-88

indicator tube

Primary measuring transducer, structurally representing a glass tube filled with granular filler (indicator powder)

Linear color indicator tube

An indicator tube that allows you to measure the concentration of a harmful substance in the analyzed air sucked through the tube along the length of the indicator powder layer in the tube that has changed its initial color

Colorimetric indicator tube

An indicator tube that makes it possible to judge the presence of a harmful substance in the analyzed air sucked through the tube at a concentration higher than the triggering concentration for this indicator tube by the color intensity of the indicator powder by comparing it with a control sample of the indicator effect

filter tube

A glass tube filled with one or more absorbers used to trap gases and vapors that interfere with the measurement of a harmful substance

indicator powder

A granular chemisorbent that changes color when a directly detectable harmful substance or its volatile products of interaction with a chemisorbent in a filter tube passes through it

Absorber

A granular sorbent or chemisorbent that completely passes the harmful substance to be determined and captures related substances that interfere with the analysis

Indication range

Range of values ​​of the scale of the indicator tube, limited by the final and initial values ​​of the scale

Lower (upper) limit

The smallest (greatest) value of the measured concentrations

Air intake device

Device for sucking air through indicator tubes

(Changed edition, Rev. No. 1)

Annex 2
(reference)

Characteristics of the produced indicator powders for equipping indicator tubes

Detected gas (steam)

Sucked air volume, cm 3

Measurement range, mg/m 3

Total air suction time, s

Gas (steam) captured by the filter cartridge

Gas (steam) interfering with the determination

nitrogen oxides

2,5-50

Halogens (chlorine, bromine, iodine), ozone in concentrations above 10 MPC

Ammonia

2,5-30

Vapors of acids

20-100

alkalis and amines

Anhydride

5-30

hydrogen sulfide,

sulfur

20-120

ammonia, nitrogen dioxide, sulfuric acid mist, water vapor

Acetylene

50-1400

Hydrogen sulfide, phosphorous

1000-3000

hydrogen, silicic hydrogen, ammonia, acetone and water vapours.

Acetone

100-2000

Sulfurous anhydride, vapors of acetic acid, acetic anhydride, hydrochloric acid, in concentrations up to 10 MPC

Pairs of ketones and esters, pairs of acetic acid, acetic anhydride, hydrochloric acid and sulfurous anhydride in concentrations above 10 MPC

Petrol

50-1000

Aromatic and unsaturated hydrocarbons, water vapor

Benzene

400 ´ 3

2-25

360 ´ 3

water vapor

xylene

25-500

water vapor

Pairs of fatty and aromatic hydrocarbons

hydrogen sulfide

5-30

Mercaptans

Toluene

25-500

water vapor

Pairs of fatty and aromatic hydrocarbons

Petroleum hydrocarbons

100-1500

Unsaturated and aromatic hydrocarbons, water vapor

Carbon oxide

5-120

Acetylene, ethylene, methane, a mixture of butane and propane, nitrogen oxides, chlorine, sulfur dioxide, hydrogen, gasoline vapors, benzene and its homologues, water, acetone, formic acid, formaldehyde, ethyl and methyl alcohols, dichloroethane, carbon disulfide

Pairs of metal carbonyls

Chlorine

0,15-15

Vapors of bromine, iodine, oxidizing agents, chloramines

Ethyl ether

100-3000

Vapors of water, ethyl alcohol, organic acids, phenol

(Revised edition, Rev. No. 1).

Annex 3
(reference)

Normalized metrological characteristics of indicator tubes and air intake devices for them

1. Metrological characteristics

1.1. For linear-color indicator tubes, the following metrological characteristics are established:

nominal static conversion characteristic,

range of measured concentrations,

basic error,

relative error,

influence functions caused by a change in the influence quantity within operating conditions.

1.2. The characteristics of indicator tubes designed to determine the presence of a harmful substance in the air of the working area (colorimetric indicator tubes) are:

the nominal value of the concentration of a harmful substance that causes the appearance of an indication effect (trigger concentration);

operation error.

1.3. For air intake devices, the following metrological characteristics are established:

the amount of air sucked in,

error in dosing the volume of sucked-in air.

Instead of volume, it is allowed to normalize the duration of suction and the volume flow of air sucked through the indicator tube.

2. Methods of normalization and forms of presentation of metrological characteristics

2.1. The nominal static conversion characteristic is presented in the form of a formula or graph, which corresponds to the scale printed on the indicator tube, cassette or special label.

2.2. The range of measured concentrations is characterized by its lower and upper limits. The lower limit of the measurement range should be no more than 0.5 of the maximum allowable concentration, and the upper limit - at least 5 maximum allowable concentrations for a given substance.

It is allowed to divide the measurement range into several sub-ranges by changing the volume of air sucked through the indicator tube, setting the nominal static conversion characteristic for each of these volumes.

If the range of indications does not coincide with the measurement range, then the range of indications is normalized by setting the initial and final values ​​of the scale.

2.3. The basic error of the indicator tubes is characterized by the limit of the permissible basic error. The values ​​of the limit of permissible basic error must be selected from the series established in GOST 8.401-80.

At the development stages of indicator tubes, their main error is characterized by:

the limit of the permissible value of the systematic component of the basic error,

the limit of the permissible value of the standard deviation of the random component of the basic error.

2.4. The number of successively used indicator tubes, which ensures the reduction of the error in the result of measuring the concentration of a harmful substance to values ​​not exceeding those specified in clause 3.7 of this standard, is established in the regulatory documentation and should not exceed 5.

2.5. The influence function is normalized in the form of a graph or table and takes into account the effect on the readings of the indicator tube of joint changes in temperature and relative humidity of the ambient air within the conditions specified in 3.1 of this standard.

The influence function is not standardized if the additional error within the conditions specified in 3.1 of this standard does not exceed 20% of the maximum permissible basic error.

2.6. The nominal value of the concentration of a harmful substance that causes the appearance of an indication effect in colorimetric indicator tubes (trigger concentration) is expressed in mg/m 3 .

2.7. The error of the colorimetric indicator tube is characterized by the limit of the permissible relative error of the response concentration. The values ​​of the limit of permissible basic error must be selected from the series established in GOST 8.401-80.

2.8. The regulatory documentation for specific indicator tubes includes data on impurities in the gas-air environment that interfere with the measurement of the concentration of this harmful substance. An impurity is considered non-interfering if, at an impurity concentration at a level of 5 maximum permissible values ​​for it, the value of the basic error of the indicator tube is less than the established limit.

2.9. The regulatory documentation for indicator tubes must specify the storage conditions and the warranty period of storage, during which the error values ​​of the indicator tubes are within the established limits.

The values ​​of the warranty period of storage of indicator tubes are selected from row 1; 1.5; 2; 3 and 5 years old.

2.10. The volume of air sucked through the indicator tube by means of an air intake device is expressed in cm 3 .

The error in dosing the volume of sucked-in air is characterized by the limit of the permissible value and is selected from a range of 5, 3, 2, 1 and 0.5%.

An air sampling device intended for use with an indicator tube must have the same flow characteristics as the air sampling device used for calibrating the indicator tube.

STATE STANDARD OF THE UNION OF THE SSR

Occupational safety standards system

Working area air

Method for measuring concentrations of harmful substances
indicator tubes

GOST 12.1.014-84

MOSCOW

APPROVED AND INTRODUCED BY Decree of the USSR State Committee for Standards dated December 14, 1984 No. 4362

INSTEAD OF GOST 12.1.014-79

The validity period was removed by decision of the Interstate Council for Standardization, Metrology and Certification (Minutes No. 5-94)

REPUBLICATION (January 1996) with Amendment No. 1 approved in March 1990 (IUS 7-90)

This International Standard establishes an accelerated method for measuring concentrations of harmful substances in the air of a working area with indicator tubes, except for the air of underground mine workings.

The essence of the method is to change the color of the indicator powder as a result of a reaction with a harmful substance (gas or steam) in the analyzed air sucked through the tube. The concentration of a harmful substance is measured by the length of the layer of indicator powder in the tube that has changed its initial color (linear-color indicator tube) or by its intensity (colorimetric indicator tube).

The terms used in the standard and their explanations are given in the appendix.

Characteristics of the produced indicator powders are given in the appendix.

The normalized metrological characteristics of indicator tubes and air intake devices for them are given in the appendix.

STATE STANDARD OF THE UNION OF THE SSR

Occupational safety standards system

Working area air

Method for measuring concentrations of harmful substances

indicatortubes

Occupational safety standards system.
Air of the work zone. Method of measuring unhealthy matters
concentration using indicator tubes

GOST
12.1.014-84

Instead
GOST 12.1.014-79

Introduction date 1986-01-01

1. EQUIPMENT

1.1. Indicator tubes, including those supplied by the consumer using special sets with indicator powders.

1.2. Filter tubes, including those supplied by the consumer using special kits.

1.3. An air intake device (such as a pump, bellows, etc.) designed for use with this indicator tube.

2. PREPARATION FOR MEASUREMENT

2.1. Preparation of equipment for measuring the concentration of harmful substances in the air of the working area is carried out in accordance with the regulatory documentation for indicator and filter tubes and the air intake device intended for them.

2.2. In unexplored production conditions, before taking measurements with indicator tubes, it is necessary to conduct a one-time qualitative assessment of the composition of the air in the working area using certified methods or guidelines approved by the USSR Ministry of Health. Based on the data obtained, the possibility of using indicator tubes for planned or operational control is established. Regardless of the composition of the air in the working area, the use of filter tubes with indicator tubes, if it is provided for in the regulatory documentation for indicator tubes, is mandatory in order to avoid violating the operating conditions of indicator tubes.

A repeated qualitative assessment of the composition of the air in the working area should be carried out with each change in production technology, which can cause the appearance of new harmful substances in the air.

2.1, 2.2 (Revised edition, Rev. No. 1).

3. MEASURING

barometric pressure - from 90 to 104 kPa (680-780 mm Hg);

relative humidity - 30 - 80%;

temperature - from 288 to 303 K.

Deviation from the specified parameters is allowed, if it is provided for in the regulatory and technical documentation for measuring instruments.

Control of the metrological parameters of the air in the working area should be carried out in parallel with measurements of the concentrations of harmful substances with indicator tubes.

3.2. An indicator tube is attached to the air intake device, designed to measure the concentration of a harmful substance, and filter tubes, if they are provided for by regulatory documentation.

The measurement should be started no later than 1 min after the depressurization of the tubes.

3.1, 3.2 (Revised edition, Rev. No. 1).

3.3. The amount of air sucked through the indicator tubes is set in accordance with the regulatory documentation for these tubes.

3.6. When the interface between the colors of the layers of the initial and reacted indicator powder is blurred, the concentration of the measured harmful substance on the scale is measured along the lower and upper parts of the boundary. The average value is taken as the measurement result.

concentration ( With m) under normal conditions in mg/m3 is calculated by the formula

where is the result of measuring the concentration of a harmful substance, at ambient temperature, t°C, relative humidity φ% and atmospheric pressure R kPa, mg/m3;

K B - coefficient that takes into account the influence of temperature and humidity of the surrounding air on the readings of indicator tubes, the value of which is determined in accordance with paragraph of the application.

The relative measurement error (δ) should not exceed ±35% in the range up to 2.0 maximum allowable concentrations (MPC) inclusive and ±25% at concentrations above 2.0 MPC under the conditions specified in paragraph .

The measurement result is presented as: ( With H ± Δ) mg/m3 with a confidence level of 0.95.

The value of the absolute error D is calculated by the formula

In the range up to 1.0 MPC, the error may increase up to ±60%. This value of the relative error must be indicated in the regulatory and technical documentation for measuring instruments.

(Revised edition, Rev. No. 1).

4. SAFETY REQUIREMENTS

4.1. When measuring the concentration of harmful substances with indicator tubes in the air of the working area, the safety standards and rules in force in this production should be observed.

4.2. Measurement of the concentration of harmful substances with indicator tubes is carried out by persons who have been trained and admitted to work on the control of harmful substances in the air of the working area.

4.3. When opening the tubes, it is necessary to observe all safety precautions when working with glass, using special devices and protective equipment.

APPLICATION 1
Reference

TERMS USED IN THE STANDARD AND THEIR EXPLANATIONS

Explanation

Work zone

Method for measuring the concentration of harmful substances

According to GOST 16263-70

harmful substance

Maximum permissible concentrations of harmful substances in the air of the working area

indicator tube

Primary measuring transducer, structurally representing a glass tube filled with granular filler (indicator powder)

Linear color indicator tube

An indicator tube that allows you to measure the concentration of a harmful substance in the analyzed air sucked through the tube along the length of the indicator powder layer in the tube that has changed its initial color

Colorimetric indicator tube

An indicator tube that makes it possible to judge the presence of a harmful substance in the analyzed air sucked through the tube at a concentration higher than the triggering concentration for this indicator tube by the color intensity of the indicator powder by comparing it with a control sample of the indicator effect

filter tube

A glass tube filled with one or more absorbers used to trap gases and vapors that interfere with the measurement of a harmful substance

indicator powder

A granular chemisorbent that changes color when a directly detectable harmful substance or its volatile products of interaction with a chemisorbent in a filter tube passes through it

Absorber

A granular sorbent or chemisorbent that completely passes the harmful substance to be determined and captures related substances that interfere with the analysis

Indication range

Range of values ​​of the scale of the indicator tube, limited by the final and initial values ​​of the scale

Lower (upper) limit

The smallest (greatest) value of the measured concentrations

Air intake device

Device for sucking air through indicator tubes

(Revised edition, Rev. No. 1).

APPLICATION 2
Reference

CHARACTERISTICS OF PRODUCED INDICATOR POWDERS FOR EQUIPMENT OF INDICATOR TUBES

Detected gas (steam)

Sucked air volume, cm3

Measurement range, mg/m3

Total air suction time, s

Gas (steam) captured by the filter cartridge

Gas (steam) interfering with the determination

nitrogen oxides

Halogens (chlorine, bromine, iodine), ozone in concentrations above 10 MPC

Pairs of acids, alkalis and amines

Sulfurous anhydride

Hydrogen sulfide, ammonia, nitrogen dioxide, sulfuric acid mist, water vapor

Acetylene

Hydrogen sulfide, hydrogen phosphide, silicic hydrogen, ammonia, acetone and water vapours.

Sulfurous anhydride, vapors of acetic acid, acetic anhydride, hydrochloric acid, in concentrations up to 10 MPC

Pairs of ketones and esters, pairs of acetic acid, acetic anhydride, hydrochloric acid and sulfurous anhydride in concentrations above 10 MPC

Aromatic and unsaturated hydrocarbons, water vapor

water vapor

water vapor

Pairs of fatty and aromatic hydrocarbons

hydrogen sulfide

Mercaptans

water vapor

Pairs of fatty and aromatic hydrocarbons

Petroleum hydrocarbons

Unsaturated and aromatic hydrocarbons, water vapor

Carbon oxide

Acetylene, ethylene, methane, a mixture of butane and propane, nitrogen oxides, chlorine, sulfur dioxide, hydrogen, gasoline vapors, benzene and its homologues, water, acetone, formic acid, formaldehyde, ethyl and methyl alcohols, dichloroethane, carbon disulfide

Pairs of metal carbonyls

Vapors of bromine, iodine, oxidizing agents, chloramines

Ethyl ether

Vapors of water, ethyl alcohol, organic acids, phenol

(Revised edition, Rev. No. 1).

APPLICATION 3
Reference

RATED METROLOGICAL CHARACTERISTICS OF INDICATOR PIPES AND AIR INTAKE DEVICES TO THEM

1. Metrological characteristics

1.1. For linear-color indicator tubes, the following metrological characteristics are established:

nominal static conversion characteristic,

range of measured concentrations,

basic error,

relative error,

influence functions caused by a change in the influence quantity within operating conditions.

1.2. The characteristics of indicator tubes designed to determine the presence of a harmful substance in the air of the working area (colorimetric indicator tubes) are:

the nominal value of the concentration of a harmful substance that causes the appearance of an indication effect (trigger concentration);

operation error.

1.3. For air intake devices, the following metrological characteristics are established:

the amount of air sucked in,

error in dosing the volume of sucked-in air.

Instead of volume, it is allowed to normalize the duration of suction and the volume flow of air sucked through the indicator tube.

2. Methods of normalization and forms of presentation of metrological characteristics

2.1. The nominal static conversion characteristic is presented in the form of a formula or graph, which corresponds to the scale printed on the indicator tube, cassette or special label.

2.2. The range of measured concentrations is characterized by its lower and upper limits. The lower limit of the measurement range should be no more than 0.5 of the maximum allowable concentration, and the upper limit - at least 5 maximum allowable concentrations for a given substance.

It is allowed to divide the measurement range into several sub-ranges by changing the volume of air sucked through the indicator tube, setting the nominal static conversion characteristic for each of these volumes.

If the range of indications does not coincide with the measurement range, then the range of indications is normalized by setting the initial and final values ​​of the scale.

2.3. The basic error of the indicator tubes is characterized by the limit of the permissible basic error. The values ​​​​of the limit of permissible basic error must be selected from the series established in GOST 8.401-80.

At the development stages of indicator tubes, their main error is characterized by:

the limit of the permissible value of the systematic component of the basic error,

the limit of the permissible value of the standard deviation of the random component of the basic error.

2.4. The number of successively used indicator tubes, which ensures the reduction of the error in the result of measuring the concentration of a harmful substance to values ​​not exceeding those specified in clause of this standard, is established in the regulatory documentation and should not exceed 5.

2.8. The regulatory documentation for specific indicator tubes includes data on impurities in the gas-air environment that interfere with the measurement of the concentration of this harmful substance. An impurity is considered non-interfering if, at an impurity concentration at a level of 5 maximum permissible values ​​for it, the value of the basic error of the indicator tube is less than the established limit.

2.9. The regulatory documentation for indicator tubes must specify the storage conditions and the warranty period of storage, during which the error values ​​of the indicator tubes are within the established limits.

The values ​​of the warranty period of storage of indicator tubes are selected from row 1; 1.5; 2; 3 and 5 years old.

2.10. The volume of air sucked through the indicator tube by means of an air intake device is expressed in cm3.

The error in dosing the volume of sucked-in air is characterized by the limit of the permissible value and is selected from a range of 5, 3, 2, 1 and 0.5%.

An air sampling device intended for use with an indicator tube must have the same flow characteristics as the air sampling device used for calibrating the indicator tube.

Interstate standard GOST 12.1.014-84
"System of labor safety standards. Air of the working area. Method for measuring the concentration of harmful substances with indicator tubes"
(approved by the Decree of the State Standard of the USSR of December 14, 1984 N 4362)

Occupational safety standards system. Air in the zone of operation. Method of measuring unhealthy matters concentration using indicator tubes.

Instead of GOST 12.1.014-79

This International Standard establishes an accelerated method for measuring concentrations of harmful substances in the air of a working area with indicator tubes, except for the air of underground mine workings.

The essence of the method is to change the color of the indicator powder as a result of a reaction with a harmful substance (gas or steam) in the analyzed air sucked through the tube. The concentration of a harmful substance is measured by the length of the layer of indicator powder in the tube that has changed its initial color (linear-color indicator tube) or by its intensity (colorimetric indicator tube).

The terms used in the standard and their explanations are given in Appendix 1.

Characteristics of the produced indicator powders are given in Appendix 2.

Standardized metrological characteristics of indicator tubes and air intake devices for them are given in Appendix 3.

1. Hardware

1.1. Indicator tubes, including those supplied by the consumer using special sets with indicator powders.

1.2. Filter tubes, including those supplied by the consumer using special kits.

1.3. An air intake device (such as a pump, bellows, etc.) designed for use with this indicator tube.

2. Preparation for measurement

2.1. Preparation of equipment for measuring the concentration of harmful substances in the air of the working area is carried out in accordance with the regulatory and technical documentation for indicator and filter tubes and the air intake device intended for them.

2.2. In unexplored production conditions, before taking measurements with indicator tubes, it is necessary to conduct a one-time qualitative assessment of the composition of the air in the working area using certified methods or guidelines approved by the USSR Ministry of Health. Based on the data obtained, the possibility of using indicator tubes for planned or operational control is established. Regardless of the composition of the air in the working area, the use of filter tubes with indicator tubes, if it is provided for in the regulatory and technical documentation for indicator tubes, is mandatory in order to avoid violating the operating conditions of indicator tubes.

A repeated qualitative assessment of the composition of the air in the working area should be carried out with each change in production technology, which can cause the appearance of new harmful substances in the air.

2.1, 2.2. (Changed edition, Rev. N 1).

3. Taking a measurement

3.1. Measurement of concentrations of harmful substances in the air of the working area is carried out with the following parameters:

barometric pressure - from 90 to 104 kPa (680-780 mm Hg);

relative humidity - 30-80%;

temperature - from 288 to 303 K.

Deviation from the specified parameters is allowed, if it is provided for in the regulatory and technical documentation for measuring instruments.

The control of meteorological parameters of the air in the working area should be carried out in parallel with the measurements of the concentrations of harmful substances with indicator tubes.

3.2. An indicator tube is attached to the air intake device, designed to measure the concentration of a harmful substance, and filter tubes, if they are provided for by regulatory and technical documentation.

The measurement should be started no later than 1 min after the depressurization of the tubes.

3.1, 3.2. (Changed edition, Rev. N 1).

3.3. The amount of air sucked through the indicator tubes is set in accordance with the normative and technical documentation for these tubes.

3.4. Measurement of concentrations of harmful substances is carried out sequentially under production conditions in accordance with GOST 12.1.005-88. In this case, the number of indicator tubes specified in the relevant regulatory and technical documentation is used.

3.5. The concentration of a harmful substance in mg / m3 in the air of the working area is measured by the length or intensity of the indicator powder layer that has changed its initial color using a scale printed on the indicator tube, cassette or special label. The measurement result is taken as the arithmetic mean of successive observations, as indicated in paragraph 3.4.

3.6. When the interface between the colors of the layers of the initial and reacted indicator powder is blurred, the concentration of the measured harmful substance on the scale is measured along the lower and upper parts of the boundary. The average value is taken as the measurement result.

3.7. The result of measuring the concentration of a harmful substance is brought to normal conditions (C_n): temperature 293 K, atmospheric pressure 101.3 kPa (760 mm Hg), relative humidity 60%.

The concentration (C_n) under normal conditions in mg/m3 is calculated by the formula

_ (273 + t) x 101.3 C \u003d C, phi, p ------------------ x K, n t 293 x p in _ where C, phi, p - the result of measuring the concentration of a harmful substance, t at ambient temperature t ° C, relative humidity fi % and atmospheric pressure p kPa, mg / m3; K - coefficient taking into account the influence of temperature and humidity of the ambient air on the indications of indicator tubes, the value of which is determined in accordance with clause 2.5 of Appendix 3.

The relative measurement error (delta) should not exceed + -35% in the range up to 2.0 maximum allowable concentrations (MAC) inclusive and + -25% at concentrations above 2.0 MAC under the conditions specified in clause 3.1.

The measurement result is presented as: (C_n+-Delta) mg/m3 with a confidence level of 0.95. The value of the absolute error (Delta) is calculated by the formula

Delta Delta = C ------. n 100

In the range up to 1.0 MPC inclusive, an increase in the error up to + -60% is allowed. This value of the relative error must be indicated in the regulatory and technical documentation for measuring instruments.

(Changed edition, Rev. N 1).

4. Safety requirements

4.1. When measuring the concentration of harmful substances with indicator tubes in the air of the working area, the safety standards and rules in force in this production should be observed.

4.2. Measurement of the concentration of harmful substances with indicator tubes is carried out by persons who have been trained and admitted to work on the control of harmful substances in the air of the working area.

4.3. When opening the tubes, it is necessary to observe all safety precautions when working with glass, using special devices and protective equipment.

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