🇵🇱 SBB LABORATORIUM BADAŃ I EKSPERTYZ PL
EnvironmentMaterials & polymers
SBB LABORATORIUM BADAŃ I EKSPERTYZ is a laboratory accredited by PCA under number AB 886 (Katowice, Poland). Its accreditation scope covers 344 test methods in the following areas: Environment, Materials & polymers. Test objects include: Waste gases, onto sorbent tubes, onto filters, Workplace environment – air – air samples collected into impingers. Most frequently used techniques: Gas chromatography with flame ionization detection (GC-FID), Spectrophotometric method, Flame atomic absorption spectrometry (FAAS).
At a glance
- Accreditation number: PCA AB 886
- Methods in scope: 344
- Types of test objects: 33
- Techniques used: 43
- City: Katowice, Poland
- Accreditation number
- AB 886
- Accreditation body
- PCA
- Address
- Sp. z o.o. Sp. K., ul. Tadeusza Boya Żeleńskiego 104, 40-750 Katowice
- City
- Katowice, Poland
What this laboratory tests (33)
- Waste gases — 129 methods
- onto sorbent tubes — 72 methods
- onto filters — 18 methods
- Workplace environment – air – air samples collected into impingers — 11 methods
- Workplace environment — 10 methods
- – air — 9 methods
- – air samples collected — 8 methods
- Workplace environment – air – air samples collected on filters — 8 methods
- Landfill gas/Biogas — 7 methods
- Workplace environment – air — 7 methods
- Workplace environment – cold microclimate — 7 methods
- Workplace environment – moderate microclimate — 6 methods
- Workplace environment – hand-arm vibration — 5 methods
- Workplace environment – hot microclimate — 5 methods
- Workplace environment – whole-body vibration — 5 methods
- and 18 more
Analytical techniques used (43)
- Gas chromatography with flame ionization detection (GC-FID) — 33 methods
- Spectrophotometric method — 21 methods
- Flame atomic absorption spectrometry (FAAS) — 15 methods
- Direct measurement method — 13 methods
- Gas chromatography with flame ionization detection (GC-FID) characteristics/method — 8 methods
- Gravimetric method — 5 methods
- Electrochemical method — 4 methods
- High-performance liquid chromatography with fluorescence detection (HPLC-FLD) — 4 methods
- Non-dispersive infrared spectrometry (NDIR) — 4 methods
- Flame atomic absorption spectrometry (FAAS) characteristics/method — 3 methods
- High-performance liquid chromatography with spectrophotometric detection (HPLC-UV) — 3 methods
- Aspiration method using absorbing solutions — 2 methods
- Aspiration method using sorption tubes — 2 methods
- Continuous flame ionization detection method (FID) — 2 methods
- Potentiometric method — 2 methods
- and 28 more
Certificate information
- Issue date
- 12.02.2026
- Issue no.
- 26
Accreditation scope — test methods (344)
| No. | Test object | Methodology / Parameters | Technique | Reference document | |
|---|---|---|---|---|---|
| Test methods | |||||
| 1 | characteristics/method | ||||
| 2 | Workplace environment – noise | A-weighted equivalent sound pressure level | PN-N-01307:1994 | PN-EN ISO 9612:2011 excluding the method covering strategy 3 - cl. 11 | ||
| 3 | Workplace environment – noise | Maximum A-weighted sound pressure level | PN-N-01307:1994 | PN-EN ISO 9612:2011 excluding the method covering strategy 3 - cl. 11 | ||
| 4 | Workplace environment – noise | C-weighted peak sound pressure level Range (25 – 136) dB |
Direct measurement method | PN-N-01307:1994 | PN-EN ISO 9612:2011 excluding the method covering strategy 3 - cl. 11 | |
| 5 | Workplace environment – noise | Noise exposure level referred to: an 8-hour daily working time the average weekly working time (calculated) |
PN-N-01307:1994 | PN-EN ISO 9612:2011 excluding the method covering strategy 3 - cl. 11 | ||
| 6 | General environment – noise from installations, equipment and industrial plants | A-weighted equivalent sound pressure level Range (25 – 135) dB |
Direct measurement method | Annex 7 to the Regulation of the Minister of Climate and Environment of 07.09.2021 (consolidated text Journal of Laws 2023 item 1706) | PN-ISO 9613-2:2002 | |
| 7 | General environment – noise from installations, equipment and industrial plants | A-weighted equivalent sound pressure level for the reference time T expressed by the indicators LAeqD and LAeqN (calculated) | Calculation method | Annex 7 to the Regulation of the Minister of Climate and Environment of 07.09.2021 (consolidated text Journal of Laws 2023 item 1706) | PN-ISO 9613-2:2002 | |
| 8 | Machinery and equipment – noise | A-weighted sound pressure level Range (25 - 135) dB |
Direct measurement method | PN-EN ISO 3746:2011/Ap1:2017-09 excluding cl. 8.4. | |
| 9 | Machinery and equipment – noise | Sound power level (calculated) | PN-EN ISO 3746:2011/Ap1:2017-09 excluding cl. 8.4. | ||
| 10 | General environment – noise from roads, railway lines, tram lines | A-weighted equivalent sound pressure level | Annex 3 to the Regulation of the Minister of the Environment of 16 June 2011 (Journal of Laws 2011 No. 140 item 824) (Journal of Laws 2011 No. 288 item 1697) excluding cl. H | ||
| 11 | General environment – noise from roads, railway lines, tram lines | A-weighted sound exposure level Range (25 – 135) dB |
Direct measurement method | Annex 3 to the Regulation of the Minister of the Environment of 16 June 2011 (Journal of Laws 2011 No. 140 item 824) (Journal of Laws 2011 No. 288 item 1697) excluding cl. H | |
| 12 | General environment – noise from roads, railway lines, tram lines | A-weighted equivalent sound level for the reference time T expressed by the indicators LAegD and LAegN (calculated) | Annex 3 to the Regulation of the Minister of the Environment of 16 June 2011 (Journal of Laws 2011 No. 140 item 824) (Journal of Laws 2011 No. 288 item 1697) excluding cl. H | ||
| 13 | Rooms in residential, collective residence and public utility buildings – noise | A-weighted equivalent sound pressure level | PN-87/B-02156 | ||
| 14 | Rooms in residential, collective residence and public utility buildings – noise | Maximum A-weighted sound pressure level Range (25 – 135) dB |
Direct measurement method | PN-87/B-02156 | |
| 15 | Rooms in residential, collective residence and public utility buildings – noise | A-weighted equivalent sound level for the reference time (calculated) characteristics/method | PN-87/B-02156 | ||
| 16 | Workplace environment - ultrasonic noise | Equivalent sound pressure levels in one-third octave bands with centre frequencies from 10 kHz to 40 kHz | PN-Z-01339:2020-12 | ||
| 17 | Workplace environment - ultrasonic noise | Maximum sound pressure levels in one-third octave bands with centre frequencies from 10 kHz to 40 kHz Range (66 – 140) dB |
Direct measurement method | PN-Z-01339:2020-12 | |
| 18 | Workplace environment - ultrasonic noise | Equivalent sound pressure levels in one-third octave bands with centre frequencies from 10 kHz to 40 kHz referred to: an 8-hour daily working time the average weekly working time (calculated) |
PN-Z-01339:2020-12 | ||
| 19 | Workplace environment – electric lighting | Illuminance Range (5 – 10000) lx |
Direct measurement method | PN-83/E-04040.03 | PN-G-02600:1996 cl. 3 | PN-G-02601:1999 cl. 3 | |
| 20 | Workplace environment – electric lighting | Illuminance uniformity (calculated) | PN-83/E-04040.03 | PN-G-02600:1996 cl. 3 | PN-G-02601:1999 cl. 3 | ||
| 21 | Workplace environment – hot microclimate | Air temperature Range (15 – 60) °C |
PN-EN ISO 7243:2018-01 | ||
| 22 | Workplace environment – hot microclimate | Natural wet bulb temperature Range (15 – 40) °C |
PN-EN ISO 7243:2018-01 | ||
| 23 | Workplace environment – hot microclimate | Black globe temperature Range (15 – 60) °C |
Direct measurement method | PN-EN ISO 7243:2018-01 | |
| 24 | Workplace environment – hot microclimate | WGBT index | PN-EN ISO 7243:2018-01 | ||
| 25 | Workplace environment – hot microclimate | WGBTeff index (calculated) | PN-EN ISO 7243:2018-01 | ||
| 26 | Workplace environment – cold microclimate | Air temperature Range (-20 – 10) °C |
PN-EN ISO 11079:2008 | ||
| 27 | Workplace environment – cold microclimate | Black globe temperature Range (-20 – 10) °C |
PN-EN ISO 11079:2008 | ||
| 28 | Workplace environment – cold microclimate | Air humidity Range (25 – 75) % |
PN-EN ISO 11079:2008 | ||
| 29 | Workplace environment – cold microclimate | Air velocity Range (0,15 – 5) m/s |
Direct measurement method | PN-EN ISO 11079:2008 | |
| 30 | Workplace environment – cold microclimate | tWC index | PN-EN ISO 11079:2008 | ||
| 31 | Workplace environment – cold microclimate | IREQmin index, | PN-EN ISO 11079:2008 | ||
| 32 | Workplace environment – cold microclimate | IREQneutral index (calculated) characteristics/method | PN-EN ISO 11079:2008 | ||
| 33 | Workplace environment – moderate microclimate | Air temperature Range (10 – 30) °C |
PN-EN ISO 7730:2006 | PN-EN ISO 7730:2006/Ap2:2016 | ||
| 34 | Workplace environment – moderate microclimate | Black globe temperature Range (10 – 30) °C |
PN-EN ISO 7730:2006 | PN-EN ISO 7730:2006/Ap2:2016 | ||
| 35 | Workplace environment – moderate microclimate | Air humidity Range (25 – 75) % |
PN-EN ISO 7730:2006 | PN-EN ISO 7730:2006/Ap2:2016 | ||
| 36 | Workplace environment – moderate microclimate | Air velocity Range (0,15 – 1,0) m/s |
Direct measurement method | PN-EN ISO 7730:2006 | PN-EN ISO 7730:2006/Ap2:2016 | |
| 37 | Workplace environment – moderate microclimate | PMV index | PN-EN ISO 7730:2006 | PN-EN ISO 7730:2006/Ap2:2016 | ||
| 38 | Workplace environment – moderate microclimate | PPD index (calculated) | PN-EN ISO 7730:2006 | PN-EN ISO 7730:2006/Ap2:2016 | ||
| 39 | Workplace environment – energy expenditure | Air temperature Range (5 – 50) °C |
PB-03 issue 9 of 24.01.2024 | ||
| 40 | Workplace environment – energy expenditure | Air flow Range (10 – 60) l/min. |
Direct measurement method | PB-03 issue 9 of 24.01.2024 | |
| 41 | Workplace environment – energy expenditure | Energy expenditure (calculated) | PB-03 issue 9 of 24.01.2024 | ||
| 42 | Workplace environment – whole-body vibration | Frequency-weighted r.m.s. vibration acceleration Range (0,05 – 100) m/s2 |
Direct measurement method | PN-EN 14253+A1:2011 | |
| 43 | Workplace environment – whole-body vibration | Daily exposure, expressed as the 8-hour energy-equivalent frequency-weighted RMS vibration acceleration dominant among the vibration accelerations determined for the three directional components taking into account the appropriate coefficients (1.4awx, | PN-EN 14253+A1:2011 | ||
| 44 | Workplace environment – whole-body vibration | 1.4awy, awz) | PN-EN 14253+A1:2011 | ||
| 45 | Workplace environment – whole-body vibration | Exposure lasting 30 minutes or less, expressed as the frequency-weighted r.m.s. vibration acceleration, dominant among the vibration accelerations determined for the three directional components with the appropriate factors applied (1.4awx, | PN-EN 14253+A1:2011 | ||
| 46 | Workplace environment – whole-body vibration | 1.4awy, awz) (calculated) characteristics/method | PN-EN 14253+A1:2011 | ||
| 47 | Workplace environment – hand-arm vibration | Frequency-weighted effective | PN-EN ISO 5349-1:2004 | PN-EN ISO 5349-2:2004 | PN-EN ISO 5349-2:2004/A1:2015 | PN-EN ISO 5349-1:2004 | ||
| 48 | Workplace environment – hand-arm vibration | vibration acceleration | PN-EN ISO 5349-2:2004 | ||
| 49 | Workplace environment – hand-arm vibration | Range (0,05 – 100) m/s2 |
Direct measurement method | PN-EN ISO 5349-2:2004/A1:2015 | |
| 50 | Workplace environment – hand-arm vibration | Daily exposure, expressed as the energy-equivalent value for an 8-hour working day of the vector sum of the frequency-corrected r.m.s. vibration accelerations, determined for the three directional components (ahwx, ahwy, ahwz). | PN-EN ISO 5349-2:2004/A1:2015 | ||
| 51 | Workplace environment – hand-arm vibration | Exposure lasting 30 minutes and less, expressed as the vector sum of root-mean-square, frequency-weighted vibration accelerations determined for the three directional components (ahwx, ahwy, ahwz) (calculated) | PN-EN ISO 5349-2:2004/A1:2015 | ||
| 52 | Rooms in residential, collective residence and public buildings – ventilation | Air stream velocity on end elements Range (0,32 – 20) m/s Range (0,50 – 25) m/s |
Measurement method with a vane anemometer; Direct measurement method - in the cross-section of the ventilation duct; Measurement method with a thermoanemometer; Direct measurement method | PN-EN 12599:2013 | |
| 53 | Rooms in residential, collective residence and public buildings – ventilation | Air volume flow rate, air change rate (calculated) | PN-EN 12599:2013 | ||
| 54 | Workplace environment – air | Crystalline silica concentration/content quartz Range (0,0073 – 1,223) mg/m3 Range (0,0050 – 0,837) mg in the sample cristobalite (0,0098 – 0,787) mg/m3 (0,0067 – 0,538) mg in the sample |
Infrared absorption spectrometry method (IR) characteristics/method | PiMOŚP 2012, No. 4(74) pp. 117-130 | |
| 55 | Workplace environment – air | Sampling for the assessment of occupational exposure to: dust agents – inhalable fraction – respirable fraction organic substances, including – inhalable fraction inorganic substances, including – inhalable fraction – respirable fraction – thoracic fraction metals and their compounds, including – inhalable fraction – respirable fraction asbestos – respirable fibres man-made mineral fibres, excluding refractory ceramic fibres – respirable fibres refractory ceramic fibres refractory ceramic fibres mixed with other man-made mineral fibres silicon carbide fibrous – respirable fibres |
Personal dosimetry method | PN-Z-04008-7:2002+Az1:2004 | |
| 56 | Workplace environment – air | Sampling for the assessment of occupational exposure to: inorganic substances, including – inhalable fraction |
Stationary method | PN-Z-04008-7:2002+Az1:2004 | |
| 57 | Workplace environment – air | Exposure index (calculated) | PN-Z-04008-7:2002+Az1:2004 | ||
| 58 | Workplace environment – air | Concentration of harmful dust agents - inhalable fraction Apatites and phosphorites Portland cement Titanium dioxide Natural graphite Synthetic graphite Amorphous and synthetic silica Wood dusts Flour dusts Dusts not classified according to toxicity Organic dusts of animal and plant origin, excluding wood and flour dusts Calcium sulfate (VI) (gypsum) Carbon black Man-made mineral fibres, except refractory ceramic fibres Talc Coal (hard, brown) Calcium magnesium carbonate (dolomite) Silicon carbide, non-fibrous Silicon carbide, fibrous Range (0,14 – 40,83) mg/m3 |
Gravimetric method characteristics/method | PN-Z-04507:2022-05 | PN-Z-04507:2022-05/Ap1:2022-08 | |
| 59 | Workplace environment – air | Concentration of dust harmful to health - respirable fraction Apatites and phosphorites Portland cement Natural graphite Amorphous and synthetic silica Organic dusts of animal and plant origin, excluding wood and flour dusts Talc Coal (hard, brown) Range (0,15 – 13,5) mg/m3 |
Gravimetric method | PN-Z-04508:2022-05 | PN-Z-04508:2022-05/Ap1:2022-08 | |
| 60 | Workplace environment – air | Carbon monoxide concentration Range (2,3 – 232) mg/m3 Range (2 – 200) ppm |
Electrochemical method | PB-01 issue 13 of 14.10.2024 | |
| 61 | Workplace environment – air – air samples collected on filters | Concentration/content of highly refined mineral oils excluding metalworking fluids inhalable fraction Range (0,15 – 7,5) mg/m3 Range (0,1 – 5) mg in the sample |
Infrared absorption spectrometry method (IR) | PN-Z-04108-5:2006 | |
| 62 | Workplace environment – air – air samples collected on filters | Hydrogen chloride concentration/content Range (0,50 – 10) mg/m3 Range (0,23 – 4,0) mg in the sample |
Turbidimetric method characteristics/method | PN-Z-04450:2014 | |
| 63 | Workplace environment – air – air samples collected into impingers | Concentration/Content of ammonia Range (1,5 – 60,0) mg/m3 Range (0,03 – 2,0) mg in the sample |
Spectrophotometric method | PN-71/Z-04041 | |
| 64 | Workplace environment – air – air samples collected into impingers | Concentration/Content of nitrogen monoxide Range (0,14 – 23,1) mg/m3 Range (0,11 – 18,6) ppm Range (0,00065 – 0,1) mg in the sample |
Spectrophotometric method | PN-Z-04009-11:2008 | |
| 65 | Workplace environment – air – air samples collected into impingers | Concentration/Content of nitrogen dioxide Range (0,22 – 35,5) mg/m3 Range (0,11 – 18,6) ppm Range (0,001 – 0,156) mg in the sample |
Spectrophotometric method | PN-Z-04009-11:2008 | |
| 66 | Workplace environment – air – air samples collected into impingers | Concentration/Content of nitric (V) acid Range (0,30 – 48,6) mg/m3 Range (0,0014 – 0,214) mg in the sample |
Spectrophotometric method | PN-Z-04009-11:2008 | |
| 67 | Workplace environment – air – air samples collected into impingers | Concentration/Content of sulphur dioxide Range (0,16 – 32) mg/m3 Range (0,06 – 12) ppm Range (0,0032 – 0,64) mg in the sample |
Spectrophotometric method | PN-Z-04015-12:1996 | |
| 68 | Workplace environment – air – air samples collected into impingers | Concentration/Content of hydrogen sulfide Range (0,7 – 16) mg/m3 Range (0,01 – 1,6) mg in the sample |
Spectrophotometric method | PN-Z-04015-13:1996 | |
| 69 | Workplace environment – air – air samples collected into impingers | Hydrogen chloride concentration/content Range (0,625 – 12,5) mg/m3 Range (0,0125 – 0,25) mg in the sample |
Turbidimetric method | PN-93/Z-04225/03 | |
| 70 | Workplace environment – air – air samples collected into impingers | Formaldehyde concentration/content Range (0,1 – 20) mg/m3 Range (0,002 – 0,4) mg in the sample |
Spectrophotometric method | PN-76/Z-04045/02 | |
| 71 | Workplace environment – air – air samples collected into impingers | Concentration/Content of chlorine Range (0,06 – 1,6) mg/m3 Range (0,001 – 0,005) mg in the sample |
Spectrophotometric method | PN-75/Z-04037/03 | |
| 72 | Workplace environment – air – air samples collected into impingers | Concentration/Content of tetraphosphorus decaoxide Range (0,07 – 2,0) mg/m3 Range (0,0014 – 0,04) mg in the sample |
Spectrophotometric method | PN-Z-04073-1:2014-08 | |
| 73 | Workplace environment – air – air samples collected into impingers | Phosphoric(V) acid concentration/content Range (0,10 – 2,5) mg/m3 Range (0,002 – 0,05) mg in the sample |
Spectrophotometric method | PN-Z-04073-1:2014-08 | |
| 74 | Workplace environment | Concentration/content of mercury, its vapours and its | PB-05 issue 4 of 03.12.2024 | ||
| 75 | – air | of inorganic compounds | PB-05 issue 4 of 03.12.2024 | ||
| 76 | – air samples collected on a filter | expressed as Hg |
PB-05 issue 4 of 03.12.2024 | ||
| 77 | and into impingers | Range (0,0006 – 0,04) mg/m3 Range (0,0001 – 0,01) mg in the sample |
Cold vapour atomic absorption spectrometry (CVAAS) characteristics/method | PB-05 issue 4 of 03.12.2024 | |
| 78 | Workplace environment – air – air samples collected on filters | Concentration/Content of antimony and its inorganic compounds, excluding stibane - calculated as Sb Range (0,015 – 1,46) mg/m3 Range (0,01 – 1,0) mg in the sample |
Flame atomic absorption spectrometry (FAAS) | PN-Z-04146-3:2006 | |
| 79 | Workplace environment – air – air samples collected on filters | Concentration/Content of chromium (metallic chromium, chromium (II), chromium (III), chromium (VI)) - calculated as Cr Range (0,007 – 7,25) mg/m3 Range (0,005 – 5,0) mg in the sample |
Flame atomic absorption spectrometry (FAAS) | PN-Z-04434:2011 | |
| 80 | Workplace environment – air – air samples collected on filters | Concentration/Content of metallic chromium, chromium (II) compounds calculated as chromium (II), chromium (III) compounds calculated as chromium (III) (calculated) | PN-Z-04434:2011 | ||
| 81 | Workplace environment – air – air samples collected on filters | Concentration/content of chromium (VI) compounds - calculated as Cr (VI) Range (0,0004 – 0,028) mg/m3 Range (0,0003 – 0,020) mg in the sample |
Spectrophotometric method | NIOSH Method 7600, Issue 3, dated 20 October 2015 | |
| 82 | Workplace environment – air – air samples collected on filters | Concentration/Content of tin and its inorganic compounds, except stannane - calculated as Sn inhalable fraction Range (0,15 – 3,65) mg/m3 Range (0,1 – 2,5) mg in the sample |
Flame atomic absorption spectrometry (FAAS) | PN-Z-04488:2017-10 | |
| 83 | Workplace environment – air – air samples collected on filters | Concentration/content of zinc oxide - calculated as Zn inhalable fraction Range (0,004 – 7,25) mg/m3 Range (0,0025 – 5,0) mg in sample |
Flame atomic absorption spectrometry (FAAS) characteristics/method | PN-87/Z-04100/03 | |
| 84 | Workplace environment | Aluminium concentration/content | PN-Z-04263-1:2012 | ||
| 85 | – air | metallic, aluminium powder | PN-Z-04263-1:2012 | ||
| 86 | – air samples collected | (unstabilised) | PN-Z-04263-1:2012 | ||
| 87 | onto filters | inhalable fraction respirable fraction |
PN-Z-04263-1:2012 | ||
| 88 | onto filters | Aluminium trioxide concentration/content calculated as Al inhalable fraction respirable fraction Range (0,03 – 7,25) mg/m3 Range (0,02 – 5,0) mg in the sample |
Flame atomic absorption spectrometry (FAAS) | PN-Z-04263-1:2012 | |
| 89 | onto filters | Aluminium hydroxide concentration/content - calculated as Al inhalable fraction respirable fraction Range (0,03 – 7,25) mg/m3 Range (0,02 – 5,0) mg in the sample |
Flame atomic absorption spectrometry method (FAAS) | PN-Z-04263-1:2012 | |
| 90 | onto filters | Concentration/content of cadmium and its inorganic compounds - calculated as Cd inhalable fraction Range (0,00035 – 0,28) mg/m3 Range (0,00025 – 0,20) mg in the sample |
Flame atomic absorption spectrometry (FAAS) | PN-Z-04102-3:2013-10 | |
| 91 | onto filters | Concentration/content of manganese and its inorganic compounds - calculated as Mn inhalable fraction respirable fraction Range (0,004 – 7,25) mg/m3 Range (0,0025 – 5,0) mg in sample |
Flame atomic absorption spectrometry (FAAS) | PN-Z-04472:2015 | |
| 92 | onto filters | Concentration/content of copper and its inorganic compounds - calculated as Cu Range (0,004 – 7,25) mg/m3 Range (0,0025 – 5,0) mg in sample |
Flame atomic absorption spectrometry (FAAS) | PN-79/Z-04106/02 | |
| 93 | onto filters | Concentration/Content of metallic nickel Range (0,0014 – 0,72) mg/m3 Range (0,001 – 0,5) mg in the sample |
PiMOŚP 2021, No. 4(110), pp. 179-189 | ||
| 94 | onto filters | Concentration/content of nickel compounds calculated as Ni – inhalable fraction (0,0014 – 0,72) mg/m3 (0,001 – 0,5) mg in the sample – respirable fraction (0,001 – 0,5) mg/m3 (0,001 – 0,5) mg in the sample |
Flame atomic absorption spectrometry (FAAS) characteristics/method | PiMOŚP 2021, No. 4(110), pp. 179-189 | |
| 95 | Workplace environment | Concentration/content of lead and its | PN-Z-04487:2017-10 | ||
| 96 | – air | of inorganic compounds | PN-Z-04487:2017-10 | ||
| 97 | – air samples collected | expressed as Pb |
PN-Z-04487:2017-10 | ||
| 98 | onto filters | – inhalable fraction Range (0,004 – 7,25) mg/m3 Range (0,003 – 5,0) mg in the sample |
Flame atomic absorption spectrometry (FAAS) | PN-Z-04487:2017-10 | |
| 99 | onto filters | Concentration/content of selenium and its compounds, except hydrogen selenide expressed as Se Range (0,01 – 1,46) mg/m3 Range (0,007 – 1,0) mg in the sample |
Flame atomic absorption spectrometry (FAAS) | PN-Z-04468:2015-10 | |
| 100 | onto filters | Silver concentration/content – inhalable fraction | PN-Z-04216-2:2012 | ||
| 101 | onto filters | Concentration/content of insoluble silver compounds expressed as Ag Range (0,003 – 0,72) mg/m3 Range (0,003 – 0,5) mg in the sample |
Flame atomic absorption spectrometry (FAAS) | PN-Z-04216-2:2012 | |
| 102 | onto filters | Concentration/content of thallium and its compounds - calculated as Tl Range (0,007 – 1,46) mg/m3 Range (0,005 – 1,0) mg in the sample |
Flame atomic absorption spectrometry (FAAS) | PN-Z-04478:2016-10 | |
| 103 | onto filters | Concentration / content of iron oxides expressed as Fe, iron (III) oxide, iron (II) oxide, triiron tetraoxide – inhalable fraction, respirable fraction Range (0,07 – 10) mg/m3 Range (0,05 – 8,0) mg in the sample |
Flame atomic absorption spectrometry (FAAS) | PN-Z-04469:2025-02 | |
| 104 | onto filters | Concentration/Content of potassium hydroxide Range (0,0104 – 10,36) mg/m3 Range (0,0072 – 7,15) mg in the sample |
Flame atomic absorption spectrometry (FAAS) | PN-Z-04436:2011 | |
| 105 | onto filters | Concentration/Content of sodium hydroxide Range (0,0145 – 14,49) mg/m3 Range (0,0100 – 10,0) mg in the sample |
Flame atomic absorption spectrometry (FAAS) | PN-Z-04435:2011 | |
| 106 | onto filters | Concentration/content of solid paraffin – inhalable fraction Range (0,07 – 10) mg/m3 Range (0,04 – 5,0) mg in the sample |
Gas chromatography with flame ionization detection (GC-FID) | PN-Z-04379:2010 | |
| 107 | onto filters | characteristics/method | 11/33 | ||
| 108 | Workplace environment | Concentration/Content: | PB-02 issue 12 of 16.10.2023 | ||
| 109 | – air | acetone |
PB-02 issue 12 of 16.10.2023 | ||
| 110 | – air samples collected | Range (0,18 – 5000) mg/m3 |
PB-02 issue 12 of 16.10.2023 | ||
| 111 | onto sorbent tubes | (0,0053 – 20) mg in the sample butan-1-ol Range (0,18 – 500) mg/m3 Range (0,0054 – 12,7) mg in the sample 2-butoxyethanol Range (0,20 – 600) mg/m3 Range (0,006 – 8) mg in the sample ethanol Range (0,36 – 5000) mg/m3 Range (0,011 – 17,6) mg in the sample 2-ethoxyethanol Range (0,19 – 50) mg/m3 Range (0,05 – 13) ppm Range (0,0058 – 9,11) mg in the sample xylene - mixture of isomers: 1,2-; |
PB-02 issue 12 of 16.10.2023 | ||
| 112 | onto sorbent tubes | 1,3-; 1,4- Range (0,33 – 1000) mg/m3 Range (0,01 – 17,8) mg in the sample 2-methylpropan-1-ol Range (0,18 – 1000) mg/m3 Range (0,0053 – 14,2) mg in the sample n-butyl acetate Range (0,17 – 3000) mg/m3 Range (0,0052 – 15,3) mg in the sample ethyl acetate Range (0,18 – 3000) mg/m3 Range (0,05 – 820) ppm Range (0,0053 – 16,1) mg in the sample toluene Range (0,17 – 1000) mg/m3 Range (0,005 – 16,9) mg in the sample |
Gas chromatography with flame ionization detection (GC-FID) | PB-02 issue 12 of 16.10.2023 | |
| 113 | onto sorbent tubes | Concentration/Content of benzene Range (0,062 – 5) mg/m3 Range (0,02 – 1,5) ppm Range (0,0018 – 1) mg in the sample |
Gas chromatography with flame ionization detection (GC-FID) | PN-Z-04016-10:2005 | |
| 114 | onto sorbent tubes | Concentration/Content of extraction naphtha Range (1,0 – 5000) mg/m3 Range (0,03 – 30) mg in the sample |
Gas chromatography with flame ionization detection (GC-FID) | PB-02 issue 12 of 16.10.2023 | PN-81/Z-04134/02 | |
| 115 | onto sorbent tubes | Concentration/Content of varnish naphtha Range (1,0 – 2000) mg/m3 Range (0,03 – 30) mg in the sample |
Gas chromatography with flame ionization detection (GC-FID) characteristics/method | PB-02 issue 12 of 16.10.2023 | PN-81/Z-04134/03 | |
| 116 | Workplace environment | Concentration/Content of butan-2-one | PB-02 issue 12 of 16.10.2023 | PN-79/Z-04107/02 | PB-02 | ||
| 117 | – air | Range (0,19 – 3000) mg/m3 |
issue 12 of 16.10.2023 | ||
| 118 | – air samples collected | (0,0058 – 30) mg in sample | PN-79/Z-04107/02 | ||
| 119 | onto sorbent tubes | Gas chromatography with flame ionization detection (GC-FID) | PN-79/Z-04107/02 | ||
| 120 | onto sorbent tubes | Concentration/Content of chloroform | PB-02 issue 12 of 16.10.2023 | PN-88/Z-04187/02 | PB-02 | ||
| 121 | onto sorbent tubes | Range (0,35 – 500) mg/m3 |
issue 12 of 16.10.2023 | ||
| 122 | onto sorbent tubes | (0,01 – 30) mg in sample | Gas chromatography with flame ionization detection (GC-FID) | PN-88/Z-04187/02 | |
| 123 | onto sorbent tubes | Concentration/Content of cyclohexane | PB-02 issue 12 of 16.10.2023 | PN-86/Z-04151/02 | PB-02 | ||
| 124 | onto sorbent tubes | Range (0,17 – 5000) mg/m3 |
issue 12 of 16.10.2023 | ||
| 125 | onto sorbent tubes | (0,005 – 30) mg in the sample | Gas chromatography with flame ionization detection (GC-FID) | PN-86/Z-04151/02 | |
| 126 | onto sorbent tubes | Concentration/Content: | PB-02 issue 12 of 16.10.2023 | PB-02 | ||
| 127 | onto sorbent tubes | cyclohexanone Range (0,22 – 500) mg/m3 Range (0,0065 – 30) mg in the sample phenol Range (0,17 – 500) mg/m3 Range (0,0050 – 13,64) mg in the sample 4-hydroxy-4-methylpentan-2-one Range (0,17 – 1000) mg/m3 Range (0,005 – 30) mg in the sample saturated acyclic isomers of hexane, excluding hexane – 2,2-dimethylbutane – 2,3-dimethylbutane – 3-methylpentane – 2-methylpentane Range (0,5 – 5000) mg/m3 Range (0,015 – 30) mg in the sample |
Gas chromatography with flame ionization detection (GC-FID) | issue 12 of 16.10.2023 | |
| 128 | onto sorbent tubes | Concentration/Content of dichloromethane Range (0,18 – 1000) mg/m3 Range (0,05 – 283) ppm Range (0,0054 – 30) mg in the sample |
Gas chromatography with flame ionization detection (GC-FID) | PN-Z-04437:2011 | |
| 129 | onto sorbent tubes | Concentration/Content of ethylbenzene | PB-02 issue 12 of 16.10.2023 | PN-79/Z-04081/01 | PB-02 | ||
| 130 | onto sorbent tubes | Range (0,17 – 1000) mg/m3 |
issue 12 of 16.10.2023 | ||
| 131 | onto sorbent tubes | (0,005 – 30) mg in the sample | Gas chromatography with flame ionization detection (GC-FID) | PN-79/Z-04081/01 | |
| 132 | onto sorbent tubes | Hexane concentration/content Range (0,17 – 1000) mg/m3 Range (0,005 – 30) mg in the sample |
Gas chromatography with flame ionization detection (GC-FID) characteristics/method | PN-Z-04136-3:2003 | |
| 133 | Workplace environment | Heptane concentration/content | PB-02 issue 12 of 16.10.2023 | PN-84/Z-04138/02 | PB-02 | ||
| 134 | – air | Range (0,17 – 5000) mg/m3 |
issue 12 of 16.10.2023 | ||
| 135 | – air samples collected | (0,005 – 30) mg in the sample | PN-84/Z-04138/02 | ||
| 136 | onto sorbent tubes | Gas chromatography with flame ionization detection (GC-FID) | PN-84/Z-04138/02 | ||
| 137 | onto sorbent tubes | Cresol concentration/content | PB-02 issue 12 of 16.10.2023 | PN-90/Z-04079/10 | PB-02 | ||
| 138 | onto sorbent tubes | (mixtures of isomers) | issue 12 of 16.10.2023 | ||
| 139 | onto sorbent tubes | Range (0,33 – 1000) mg/m3 Range (0,01 – 15,2) mg in the sample |
Gas chromatography with flame ionization detection (GC-FID) | PN-90/Z-04079/10 | |
| 140 | onto sorbent tubes | Cumene concentration/content Range (0,17 – 1000) mg/m3 Range (0,005 – 30) mg in the sample |
Gas chromatography with flame ionization detection (GC-FID) | PN-Z-04016-6:1998 | |
| 141 | onto sorbent tubes | Concentration/Content | PB-02 issue 12 of 16.10.2023 | PN-92/Z-04113/09 | PB-02 | ||
| 142 | onto sorbent tubes | methyl methacrylate | issue 12 of 16.10.2023 | ||
| 143 | onto sorbent tubes | Range (0,17 – 1000) mg/m3 Range (0,005 – 30) mg in the sample |
Gas chromatography with flame ionization detection (GC-FID) | PN-92/Z-04113/09 | |
| 144 | onto sorbent tubes | Concentration/Content of methanol Range (0,60 – 1200) mg/m3 Range (0,0054 – 20) mg in the sample |
Gas chromatography with flame ionization detection (GC-FID) | PN-Z-04476:2016 | |
| 145 | onto sorbent tubes | Concentration/Content | PB-02 issue 12 of 16.10.2023 | PN-84/Z-04137/02 | PB-02 | ||
| 146 | onto sorbent tubes | methylcyclohexane | issue 12 of 16.10.2023 | ||
| 147 | onto sorbent tubes | Range (0,17 – 6000) mg/m3 Range (0,005 – 30) mg in the sample |
Gas chromatography with flame ionization detection (GC-FID) | PN-84/Z-04137/02 | |
| 148 | onto sorbent tubes | Concentration/Content | NIOSH Method 1302, Issue 1, dated 15 January 1998 | NIOSH Method 1302, | ||
| 149 | onto sorbent tubes | 1- methyl-2-pyrrolidone Range (0,07 – 360) mg/m3 Range (0,02 – 87) ppm Range (0,0050 – 10,0) mg in the sample |
Gas chromatography with flame ionization detection (GC-FID) | Issue 1, dated 15 January 1998 | |
| 150 | onto sorbent tubes | Concentration/Content | PB-02 issue 12 of 16.10.2023 | PN-86/Z-04165/02 | PB-02 | ||
| 151 | onto sorbent tubes | 4-methylpentan-2-one | issue 12 of 16.10.2023 | ||
| 152 | onto sorbent tubes | Range (0,17 – 1000) mg/m3 Range (0,005 – 30) mg in the sample |
Gas chromatography with flame ionization detection (GC-FID) | PN-86/Z-04165/02 | |
| 153 | onto sorbent tubes | Concentration/Content | PN-Z-04354:2005 | ||
| 154 | onto sorbent tubes | 1-methoxypropan-2-ol Range (0,18 – 1000) mg/m3 Range (0,0054 – 30) mg in the sample |
Gas chromatography with flame ionization detection (GC-FID) characteristics/method | PN-Z-04354:2005 | |
| 155 | Workplace environment | Concentration/Content of kerosene | PB-02 issue 12 of 16.10.2023 | PN-92/Z-04227/02 | PB-02 | ||
| 156 | – air | Range (1,0 – 1000) mg/m3 |
issue 12 of 16.10.2023 | ||
| 157 | – air samples collected | (0,03 – 30) mg in the sample | PN-92/Z-04227/02 | ||
| 158 | onto sorbent tubes | Gas chromatography with flame ionization detection (GC-FID) | PN-92/Z-04227/02 | ||
| 159 | onto sorbent tubes | 2-Methoxy-1-methylethyl acetate concentration/content Range (0,18 – 1000) mg/m3 Range (0,0054 – 30) mg in the sample |
Gas chromatography with flame ionization detection (GC-FID) | PN-Z-04119-10:2008 | |
| 160 | onto sorbent tubes | Vinyl acetate concentration/content | PB-02 issue 12 of 16.10.2023 | PN-87/Z-04178/02 | PB-02 | ||
| 161 | onto sorbent tubes | Range (0,19 – 1000) mg/m3 |
issue 12 of 16.10.2023 | ||
| 162 | onto sorbent tubes | (0,0057 – 30) mg in the sample | Gas chromatography with flame ionization detection (GC-FID) | PN-87/Z-04178/02 | |
| 163 | onto sorbent tubes | Octane concentration/content | PB-02 issue 12 of 16.10.2023 | PN-86/Z-04166/02 | PB-02 | ||
| 164 | onto sorbent tubes | Range (0,17 – 5000) mg/m3 |
issue 12 of 16.10.2023 | ||
| 165 | onto sorbent tubes | (0,005 – 30) mg in the sample | Gas chromatography with flame ionization detection (GC-FID) | PN-86/Z-04166/02 | |
| 166 | onto sorbent tubes | Propan-2-ol concentration/content Range (0,17 – 2500) mg/m3 Range (0,0050 – 20) mg in the sample |
Gas chromatography with flame ionization detection (GC-FID) | PN-Z-04535:2022-01 | |
| 167 | onto sorbent tubes | Styrene concentration/content | PB-02 issue 12 of 16.10.2023 | PN-86/Z-04152/02 | PB-02 | ||
| 168 | onto sorbent tubes | Range (0,17 – 1000) mg/m3 |
issue 12 of 16.10.2023 | ||
| 169 | onto sorbent tubes | (0,005 – 30,0) mg in the sample | Gas chromatography with flame ionization detection (GC-FID) | PN-86/Z-04152/02 | |
| 170 | onto sorbent tubes | Tetrachloroethene concentration/content | PB-02 issue 12 of 16.10.2023 | PN-78/Z-04118/01 | PB-02 | ||
| 171 | onto sorbent tubes | Range (0,17 – 1000) mg/m3 |
issue 12 of 16.10.2023 | ||
| 172 | onto sorbent tubes | (0,03 – 145) ppm (0,005 – 30) mg in the sample | Gas chromatography with flame ionization detection (GC-FID) | PN-78/Z-04118/01 | |
| 173 | onto sorbent tubes | Trichloroethene concentration/content | PB-02 issue 12 of 16.10.2023 | PN-78/Z-04047/02 | PB-02 | ||
| 174 | onto sorbent tubes | Range (0,17 – 500) mg/m3 |
issue 12 of 16.10.2023 | ||
| 175 | onto sorbent tubes | (0,005 – 15) mg in the sample | Gas chromatography with flame ionization detection (GC-FID) characteristics/method | PN-78/Z-04047/02 | |
| 176 | Workplace environment | Concentration/Content: | PN-Z-04016-4:1998 | ||
| 177 | – air | 1,2,3-trimethylbenzene |
PN-Z-04016-4:1998 | ||
| 178 | – air samples collected | Range (0,17 – 1000) mg/m3 |
PN-Z-04016-4:1998 | ||
| 179 | onto sorbent tubes | (0,005 – 30) mg in the sample 1,2,4-trimethylbenzene Range (0,17 – 1000) mg/m3 Range (0,005 – 30) mg in the sample 1,3,5-trimethylbenzene Range (0,17 – 1000) mg/m3 Range (0,005 – 30) mg in the sample trimethylbenzene – mixture isomers 1,2,3-;1,2,4-;1,3,5- Range (0,33 – 1000) mg/m3 Range (0,01 – 30) mg in sample |
Gas chromatography with flame ionization detection (GC-FID) | PN-Z-04016-4:1998 | |
| 180 | onto sorbent tubes | Concentration/Content of acetic acid Range (1,0 – 400) mg/m3 Range (0,04 – 160) ppm Range (0,05 – 20) mg in the sample |
Gas chromatography with flame ionization detection (GC-FID) | PN-Z-04323:2004 | |
| 181 | onto sorbent tubes | Propan-1-ol concentration/content Range (0,33 – 2000) mg/m3 Range (0,01 – 20) mg in the sample |
Gas chromatography with flame ionization detection (GC-FID) | PN-Z-04224-3:2003 | |
| 182 | onto sorbent tubes | Pentane concentration/content Range (0,33 – 6000) mg/m3 Range (0,01 – 50) mg in the sample |
Gas chromatography with flame ionization detection (GC-FID) | PN-Z-04318:2005 | |
| 183 | onto sorbent tubes | Concentration/Content | PN-Z-04399:2011 | ||
| 184 | onto sorbent tubes | 2-(2-butoxyethoxy)ethanol Range (0,86 – 300) mg/m3 Range (0,025 – 10) mg in the sample |
Gas chromatography with flame ionization detection (GC-FID) | PN-Z-04399:2011 | |
| 185 | onto sorbent tubes | 2-Butoxyethyl acetate concentration/content Range (0,21 – 300) mg/m3 Range (0,006 – 10) mg in the sample |
Gas chromatography with flame ionization detection (GC-FID) | PN-Z-04304:2003 | |
| 186 | onto sorbent tubes | Formaldehyde concentration/content Range (0,007 – 40) mg/m3 Range (0,0001 – 0,1) mg in the sample |
High-performance liquid chromatography with spectrophotometric detection (HPLC-UV) characteristics/method | PiMOŚP 1999, No. 22, pp. 96-100 | |
| 187 | Workplace environment | Concentration/Content of acrylaldehyde | PN-Z-04045-16:2010 | ||
| 188 | – air | Range (0,003 – 2,7) mg/m3 |
PN-Z-04045-16:2010 | ||
| 189 | – air samples collected | (0,00005 – 0,04) mg in the sample | PN-Z-04045-16:2010 | ||
| 190 | onto sorbent tubes | High-performance liquid chromatography with spectrophotometric detection (HPLC-UV) | PN-Z-04045-16:2010 | ||
| 191 | onto sorbent tubes | Concentration/Content fluorides expressed as F- Range (0,0035 – 4,3) mg/m3 Range (0,0025 – 3,1) mg in the sample hydrogen fluoride Range (0,0036 – 4,4) mg/m3 Range (0,0026 – 3,3) mg in the sample |
Potentiometric method | NIOSH Method 7902 Issue 2, dated 15 August 1994 | |
| 192 | onto sorbent tubes | Concentration/Content of benzo(a)pyrene Range (0,00002 – 0,03) mg/m3 Range (0,01 – 22) μg in the sample |
High-performance liquid chromatography method (HPLC) | PN-Z-04240-2:1999 | |
| 193 | onto sorbent tubes | Concentration/Content of dibenzo(a,h)anthracene Range (0,00003 – 0,030) mg/m3 Range (0,02 – 22) μg in the sample |
High-performance liquid chromatography with fluorescence detection (HPLC-FLD) | PN-Z-04240-4:1999 | |
| 194 | onto sorbent tubes | Concentration/Content toluene-2,4-diyl diisocyanate (toluene 2,4-diisocyanate); 2,4-TDI) Range (0,0003 – 0,28) mg/m3 Range (0,05 – 50) μg in the sample toluene-2,6-diyl diisocyanate (toluene 2,6-diisocyanate; 2,6-TDI) Range (0,0003 – 0,28) mg/m3 Range (0,05 – 50) μg in the sample |
High-performance liquid chromatography with fluorescence detection (HPLC-FLD) | PN-Z-04490:2017 | |
| 195 | onto sorbent tubes | Concentration/Content methylenebis(phenyl isocyanate) (4,4-methylenebis(phenyl isocyanate); |
PB-17 issue 2 of 26.11.2021 | ||
| 196 | onto sorbent tubes | MDI) Range (0,0003 – 0,28) mg/m3 Range (0,05 – 50) μg in the sample hexane-1,6-diyl diisocyanate, (1,6-hexamethylene diisocyanate; 1,6- |
PB-17 issue 2 of 26.11.2021 | ||
| 197 | onto sorbent tubes | HDI) Range (0,0006 – 0,28) mg/m3 Range (0,10 – 50) μg in the sample |
High-performance liquid chromatography with fluorescence detection (HPLC-FLD) characteristics/method | PB-17 issue 2 of 26.11.2021 | |
| 198 | Workplace environment | Concentration/Content | PN-Z-04240-5:2006 | ||
| 199 | - air | polycyclic hydrocarbons | PN-Z-04240-5:2006 | ||
| 200 | - air samples collected on | aromatic (PAH) | PN-Z-04240-5:2006 | ||
| 201 | filters and sorbent tubes | naphthalene (0,00005 – 0,04) mg/m3 Range (0,03 – 24) μg in the sample acenaphthylene (0,00004 – 0,04) mg/m3 (0,02 – 22) μg in the sample acenaphthene (0,00005 – 0,04) mg/m3 (0,03 – 23) μg in the sample fluorene (0,00002 – 0,04) mg/m3 (0,01 – 23) μg in sample phenanthrene (0,00004 – 0,04) mg/m3 (0,02 – 22) μg in sample anthracene (0,00002 – 0,04) mg/m3 (0,01 – 23) μg in sample fluoranthene (0,00004 – 0,04) mg/m3 (0,02 – 23) μg in sample pyrene (0,00004 – 0,04) mg/m3 (0,02 – 23) μg in the sample benzo(a)anthracene (0,00004 – 0,04) mg/m3 (0,02 – 22) μg in the sample chrysene (0,00002 – 0,04) mg/m3 (0,01 – 23) μg in sample benzo(b)fluoranthene (0,00004 – 0,04) mg/m3 (0,02 – 23) μg in sample benzo(k)fluoranthene (0,00004 – 0,04) mg/m3 (0,02 – 22) μg in the sample benzo(a)pyrene (0,00002 – 0,04) mg/m3 (0,01 – 22) μg in the sample dibenzo(a,h)anthracene (0,00004 – 0,04) mg/m3 (0,02 – 22) μg in the sample benzo(g,h,i)perylene (0,00005 – 0,04) mg/m3 (0,03 – 22) μg in the sample indeno (1,2,3-cd)pyrene (0,00005 – 0,04) mg/m3 (0,03 – 22) μg in the sample |
High-performance liquid chromatography with fluorescence and ultraviolet detection (HPLC-FLD/UV) | PN-Z-04240-5:2006 | |
| 202 | filters and sorbent tubes | Polycyclic aromatic hydrocarbons (anthracene, benzo(a)anthracene, chrysene, benzo(b)fluoranthene, benzo(k)fluoranthene, benzo(a)pyrene, dibenzo(a,h)anthracene, benzo(g,h,i)perylene, indeno(1,2,3cd)pyrene) as the sum of the products of concentrations and carcinogenicity factors of the 9 carcinogenic PAHs (calculated) characteristics/method | PN-Z-04240-5:2006 | ||
| 203 | Waste gas abatement equipment | Concentration of organic substances in the form of gases and vapours expressed as total gaseous organic carbon Range (2,0 – 1000) mg/m3 |
Continuous flame ionization detection method (FID) | PB-14 issue 5 of 14.01.2022 | PN-EN 12619:2013-05 | |
| 204 | Waste gas abatement equipment | Reduction of the concentration of organic substances in the form of gases and vapours expressed as total gaseous organic carbon (calculated) | PB-14 issue 5 of 14.01.2022 | PN-EN 12619:2013-05 | ||
| 205 | Waste gas dedusting equipment | Dust concentration Range (0,001 – 100) g/m3 |
Gravimetric method | PN-M-34129:1987 – Method A | PN-Z-04030-7:1994 | |
| 206 | Waste gas dedusting equipment | Dedusting efficiency (calculated) characteristics/method | PN-M-34129:1987 – Method A | PN-Z-04030-7:1994 | ||
| 207 | Waste gases | Sampling for determination of dust concentration | PN-Z-04030-7:1994 | ||
| 208 | Waste gases | Volume flow rate for dynamic pressures > 10 Pa | Stagnation pressure method | PN-Z-04030-7:1994 | |
| 209 | Waste gases | Dust concentration Range (0,001 – 100) g/m3 |
Gravimetric method | PN-Z-04030-7:1994 | |
| 210 | Waste gases | Dust emission (calculated) | PN-Z-04030-7:1994 | ||
| 211 | Waste gases | Sampling for determination of dust concentration | PN-EN 13284-1:2018-02 | ||
| 212 | Waste gases | Dust concentration Range (0,0005 – 0,050) g/m3 |
Gravimetric method | PN-EN 13284-1:2018-02 | |
| 213 | Waste gases | Dust emission (calculated) | PN-EN 13284-1:2018-02 | ||
| 214 | Waste gases | Water vapour concentration (H2O) Range (29 – 250) g/m3 Range (4,0 – 40) % vol. |
Condensation-adsorption method | PN-EN 14790:2017-04 | |
| 215 | Waste gases | Oxygen concentration | PN-ISO 10396:2001 | PN-EN 14789:2017-04 | ||
| 216 | Waste gases | O2 (3,0 – 21) % | Paramagnetic method | PN-ISO 10396:2001 | PN-EN 14789:2017-04 | |
| 217 | Waste gases | Concentration of carbon monoxide, nitrogen monoxide, carbon dioxide, nitrogen dioxide, sulphur dioxide, oxygen, nitrogen oxides | PN-ISO 10396:2001 | ||
| 218 | Waste gases | CO (3,0 – 1250) mg/m3 | PN-ISO 10396:2001 | ||
| 219 | Waste gases | NO (4,0 – 1206) mg/m3 | PN-ISO 10396:2001 | ||
| 220 | Waste gases | CO2 (0,1 – 21) % | PN-ISO 10396:2001 | ||
| 221 | Waste gases | NO2 (8,0 – 820) mg/m3 | PN-ISO 10396:2001 | ||
| 222 | Waste gases | SO2 (8,0 – 1430) mg/m3 | Non-dispersive infrared spectrometry (NDIR) | PN-ISO 10396:2001 | |
| 223 | Waste gases | O2 (1,4 – 21) % | Electrochemical method | PN-ISO 10396:2001 | |
| 224 | Waste gases | NOx concentration Range (3,0 – 1600) mg/m3 |
Chemiluminescence method (CLD) | PN-ISO 10396:2001 | |
| 225 | Waste gases | Emission of CO, NO, CO2, NO2, SO2, NOx (NO and NO2 calculated as NO2) (calculated) | PN-ISO 10396:2001 | ||
| 226 | Waste gases | Concentration of organic substances in the form of gases and vapours expressed as total gaseous organic carbon Range (2,0 – 1000) mg/m3 |
Continuous flame ionization detection method (FID) | PN-EN 12619:2013-05 | |
| 227 | Waste gases | Emission of organic substances in the form of gases and vapours expressed as total gaseous organic carbon (calculated) characteristics/method | PN-EN 12619:2013-05 | ||
| 228 | Waste gases | Sampling for the determination of PCDD/PCDF concentration | PN-EN 1948-1:2006+Ap1:2017-08 | ||
| 229 | Waste gases | PCDD/PCDF emission (calculated) | PN-EN 1948-1:2006+Ap1:2017-08 | ||
| 230 | Waste gases | Sampling for determination of the concentration of individual gaseous organic compounds | PN-EN 13649:2005 | ||
| 231 | Waste gases | Sum of volatile organic compounds (calculated) | PN-EN 13649:2005 | ||
| 232 | Waste gases | Emission of individual gaseous organic compounds (calculated) | PN-EN 13649:2005 | ||
| 233 | Waste gases | Sum of aliphatic hydrocarbons from | PN-EN 13649:2005 | ||
| 234 | Waste gases | C5-C13 (calculated) | PN-EN 13649:2005 | ||
| 235 | Waste gases | Sum of aromatic hydrocarbons (calculated) | PN-EN 13649:2005 | ||
| 236 | Concentration/Content: Range: - acetone (0,09 – 2000) mg/m3 (0,0053 – 30) mg in sample - benzene (0,08 – 2000) mg/m3 (0,005 – 30) mg in sample - butan-1-ol (0,09 – 2000) mg/m3 (0,0054 – 30) mg in sample - butan-2-one (0,10 – 2000) mg/m3 (0,0058 – 30) mg in sample - 2-butoxyethanol (0,10 – 2000) mg/m3 (0,006 – 30) mg in sample - chloroform (0,17 - 2000) mg/m3 (0,01 – 30) mg in sample - cyclohexane (0,08 – 2000) mg/m3 (0,005 – 30) mg in sample - cyclohexanone (0,11 – 2000) mg/m3 (0,0065 – 30) mg in sample - dichloromethane (0,08 – 2000) mg/m3 (0,0054 – 30) mg in sample - ethanol (0,18 – 2000) mg/m3 (0,011 – 30) mg in sample - 2-ethoxyethanol (0,10 – 2000) mg/m3 (0,0058 – 30) mg in sample - ethylbenzene (0,08 – 2000) mg/m3 (0,005 – 30) mg in sample, Gas chromatography with flame ionisation detection (GC-FID) | Concentration/Content: acetone (0,09 – 2000) mg/m3 Range (0,0053 – 30) mg in sample benzene (0,08 – 2000) mg/m3 (0,005 – 30) mg in the sample butan-1-ol (0,09 – 2000) mg/m3 (0,0054 – 30) mg in the sample butan-2-one (0,10 – 2000) mg/m3 (0,0058 – 30) mg in sample 2-butoxyethanol (0,10 – 2000) mg/m3 (0,006 – 30) mg in the sample (0,17 - 2000) mg/m3 (0,01 – 30) mg in sample cyclohexane (0,08 – 2000) mg/m3 (0,005 – 30) mg in the sample cyclohexanone (0,11 – 2000) mg/m3 (0,0065 – 30) mg in the sample dichloromethane (0,08 – 2000) mg/m3 (0,0054 – 30) mg in the sample ethanol (0,18 – 2000) mg/m3 (0,011 – 30) mg in the sample 2-ethoxyethanol (0,10 – 2000) mg/m3 (0,0058 – 30) mg in sample ethylbenzene (0,08 – 2000) mg/m3 (0,005 – 30) mg in the sample |
Gas chromatography with flame ionization detection (GC-FID) characteristics/method | PN-EN 13649:2005 | |
| 237 | Waste gases | Concentration/Content: hexane Range (0,08 – 2000) mg/m3 Range (0,005 – 30) mg in the sample acyclic saturated hexane isomers: – 2,2-dimethylbutane – 2,3-dimethylbutane – 3-methylpentane – 2-methylpentane (0,17 – 2000) mg/m3 (0,01 – 30) mg heptane (0,08 – 2000) mg/m3 (0,005 – 30) mg in the sample 4-hydroxy-4-methylpentan-2-one (0,08 – 2000) mg/m3 (0,005 – 30) mg in the sample xylene (mixture of isomers) (0,17 – 2000) mg/m3 (0,01 – 30) mg in sample cumene (0,08 – 2000) mg/m3 (0,005 – 30) mg in the sample methyl methacrylate (0,08 – 2000) mg/m3 (0,005 – 30) mg in the sample methanol (0,27 – 2000) mg/m3 (0,0054 – 20) mg in the sample methylcyclohexane (0,08 – 2000) mg/m3 (0,005 – 30) mg in the sample 1-methyl-2-pyrrolidone (0,08 – 2000) mg/m3 (0,0050 – 10,0) mg in the sample 4-methylpentan-2-one (0,08 – 2000) mg/m3 (0,005 – 30) mg in the sample 2-methylpropan-1-ol (0,09 – 2000) mg/m3 (0,0053 – 30) mg in sample 1-methoxypropan-2-ol (0,09 – 2000) mg/m3 (0,0054 – 30) mg in the sample butyl acetate (0,09 – 2000) mg/m3 (0,0052 – 30) mg in the sample ethyl acetate (0,09 – 2000) mg/m3 (0,0053 – 30) mg in sample |
Gas chromatography with flame ionization detection (GC-FID) characteristics/method | PN-EN 13649:2005 | |
| 238 | Waste gases | Concentration/Content: 2-methoxy-1-methylethyl acetate (0,09 – 2000) mg/m3 (0,0054 – 30) mg in the sample vinyl acetate (0,10 – 2000) mg/m3 (0,0057 – 30) mg in the sample propan-2-ol (0,08 – 2000) mg/m3 (0,0050 – 20) mg in the sample propylbenzene (0,08 – 2000) mg/m3 (0,005 – 30) mg in the sample styrene (0,08 – 2000) mg/m3 (0,005 – 30) mg in the sample tetrachloroethene (0,08 – 2000) mg/m3 (0,005 – 30) mg in the sample toluene (0,08 – 2000) mg/m3 (0,005 – 30) mg in the sample trichloroethene (0,08 – 2000) mg/m3 (0,005 – 15) mg in the sample 1,2,3 trimethylbenzene (0,08 – 2000) mg/m3 (0,005 – 30) mg in the sample 1,2,4 trimethylbenzene (0,08 – 2000) mg/m3 (0,005 – 30) mg in the sample 1,3,5 trimethylbenzene (0,08 – 2000) mg/m3 (0,005 – 30) mg in the sample octane (0,08 – 2000) mg/m3 (0,005 – 30) mg in the sample nonane (0,08 – 2000) mg/m3 (0,005 – 30) mg in the sample decane (0,08 – 2000) mg/m3 (0,005 – 30) mg in the sample undecane (0,08 – 2000) mg/m3 (0,005 – 30) mg in the sample dodecane (0,08 – 2000) mg/m3 (0,005 – 30) mg in the sample tridecane (0,08 – 2000) mg/m3 (0,005 – 30) mg in the sample |
Gas chromatography with flame ionization detection (GC-FID) characteristics/method | PN-EN 13649:2005 | |
| 239 | Waste gases | Concentration/Content: pentane (0,17 – 3500) mg/m3 (0,01 – 50) mg in the sample propan-1-ol (0,17 – 2000) mg/m3 (0,01 – 20) mg in the sample 2 (2-butoxyethoxy)ethanol (0,42 – 2000) mg/m3 (0,025 – 20) mg in the sample 2-butoxyethyl acetate (0,10 – 2000) mg/m3 (0,006 – 20) mg in the sample |
Gas chromatography with flame ionization detection (GC-FID) | PN-EN 13649:2005 | |
| 240 | Waste gases | Sampling for determination of hydrogen chloride concentration | PN-EN 1911:2011 | ||
| 241 | Waste gases | Hydrogen chloride concentration/content Range (0,25 – 500) mg/m3 Range (0,050 – 30,0) mg in the sample |
Spectrophotometric method | PN-EN 1911:2011 | |
| 242 | Waste gases | Hydrogen chloride emission (calculated) | PN-EN 1911:2011 | ||
| 243 | Waste gases | Sampling for determination of hydrogen fluoride concentration | ISO 15713:2006 | ||
| 244 | Waste gases | Hydrogen fluoride emission (calculated) | ISO 15713:2006 | ||
| 245 | Waste gases | Sampling for determination of metal concentrations: As, Cd, Cr, Co, Cu, | PN-EN 14385:2005 | ||
| 246 | Waste gases | Mn, Ni, Pb, Sb, Tl, V | PN-EN 14385:2005 | ||
| 247 | Waste gases | Concentration/Content: antimony (0,005 – 0,7) mg/m3 Range (0,01 – 1,0) mg in the sample arsenic (0,005 – 5,0) mg/m3 (0,075 – 0,5) mg in the sample chromium (0,005 – 5,0) mg/m3 (0,005 – 5,0) mg in the sample manganese (0,005 – 5,0) mg/m3 (0,0025 – 5,0) mg in sample nickel (0,005 – 0,5) mg/m3 (0,005 – 0,5) mg in the sample cadmium (0,005 – 0,5) mg/m3 (0,0005 – 0,5) mg in the sample copper (0,005 – 5,0) mg/m3 (0,0025 – 5,0) mg in sample lead (0,005 – 5,0) mg/m3 (0,002 – 5,0) mg in the sample thallium (0,005 – 0,7) mg/m3 (0,005 – 1,0) mg in the sample |
Flame atomic absorption spectrometry (FAAS) | PN-EN 14385:2005 | |
| 248 | Waste gases | Emission of metals: As, Cd, Cr, Co, Cu, Mn, | PN-EN 14385:2005 | ||
| 249 | Waste gases | Ni, Pb, Sb, Tl, V (calculated) characteristics/method | PN-EN 14385:2005 | ||
| 250 | Waste gases | Sampling for the determination of mercury concentration | PN-EN 13211+AC:2006 | ||
| 251 | Waste gases | Mercury emission (calculated) | PN-EN 13211+AC:2006 | ||
| 252 | Waste gases | Mercury concentration/content Range (0,00001 – 1,67) mg/m3 Range (0,0001 – 0,050) mg in the sample |
Cold vapour atomic absorption spectrometry (CVAAS) | PN-EN 13211+AC:2006 | |
| 253 | Waste gases | Sampling for determination of SO2 concentration | PN-EN 14791:2017-04 | ||
| 254 | Waste gases | SO2 emission (calculated) | PN-EN 14791:2017-04 | ||
| 255 | Waste gases | Concentration/Content of sulphur dioxide Range (1,4 – 2000) mg/m3 Range (0,25 – 64) mg in the sample |
Thoron method | PN-EN 14791:2017-04 | |
| 256 | Waste gases | Concentration of nitrogen monoxide, nitrogen oxides | PN-ISO 10396:2001 | PN-EN 14792:2017-04 | ||
| 257 | Waste gases | NO (2,0 – 1200) mg/m3 | PN-ISO 10396:2001 | PN-EN 14792:2017-04 | ||
| 258 | Waste gases | NOx (3,0 – 1600) mg/m3 | Chemiluminescence method | PN-ISO 10396:2001 | PN-EN 14792:2017-04 | |
| 259 | Waste gases | Emission of NO, NOx (NO and NO2 calculated as NO2 ) (calculated) | PN-ISO 10396:2001 | PN-EN 14792:2017-04 | ||
| 260 | Waste gases | Carbon monoxide concentration Range (3,0 – 1250) mg/m3 |
Non-dispersive infrared spectrometry (NDIR) | PN-ISO 10396:2001 | PN-ISO 15058:2017-04 | |
| 261 | Waste gases | CO emission (calculated) | PN-ISO 10396:2001 | PN-ISO 15058:2017-04 | ||
| 262 | Waste gases | Carbon dioxide concentration Range (0,2 – 21) % |
Non-dispersive infrared spectrometry (NDIR) | PN-ISO 10396:2001 | ISO 12039:2019 | |
| 263 | Waste gases | Emission of CO2 (calculated) characteristics/method | PN-ISO 10396:2001 | ISO 12039:2019 | ||
| 264 | Waste gases | Sampling of PM-10 dust, | PN-EN ISO 23210:2010 | ||
| 265 | Waste gases | PM-2,5 for testing | PN-EN ISO 23210:2010 | ||
| 266 | Waste gases | PM-10, PM-2,5 dust concentration Range (0,4 – 40) mg/m3 |
Gravimetric method | PN-EN ISO 23210:2010 | |
| 267 | Waste gases | PM10, PM2,5 dust emission (calculated) | PN-EN ISO 23210:2010 | ||
| 268 | Waste gases | Sampling for determination of | PB-09 issue 18 of 10.10.2024 | PB-09 | ||
| 269 | Waste gases | isocyanate concentrations | issue 18 of 10.10.2024 | ||
| 270 | Waste gases | Isocyanate emission (calculated) | issue 18 of 10.10.2024 | ||
| 271 | Waste gases | Sampling for determination of hydrogen cyanide concentration | issue 18 of 10.10.2024 | ||
| 272 | Waste gases | Emission of hydrogen cyanide (calculated) | issue 18 of 10.10.2024 | ||
| 273 | Waste gases | Gas sampling | Aspiration method using Tedlar bags | issue 18 of 10.10.2024 | |
| 274 | Waste gases | Sampling for determination of metal concentrations: Sn, Zn, Al, Fe, Ag, Se | Aspiration method using filters and absorbing solutions | issue 18 of 10.10.2024 | |
| 275 | Waste gases | Emission of metals: Sn, Zn, Al, Fe, Ag, Se (calculated) | issue 18 of 10.10.2024 | ||
| 276 | Waste gases | Sampling for determination of the concentration of KOH, NaOH | Aspiration method using filters | issue 18 of 10.10.2024 | |
| 277 | Waste gases | Emission of KOH, NaOH (calculated) | issue 18 of 10.10.2024 | ||
| 278 | Waste gases | Sampling for determination of the concentration of phenol and cresol (mixture of isomers) | PB-09 issue 18 of 10.10.2024 | ||
| 279 | Waste gases | Emission of phenol, cresol (mixture of isomers) (calculated) | PB-09 issue 18 of 10.10.2024 | ||
| 280 | Waste gases | Concentration/Content tin (0,005 – 0,83) mg/m3 Range (0,05 – 0,5) mg in the sample zinc (0,005 – 5,0) mg/m3 (0,0025 – 5,0) mg in sample aluminium (0,005 – 5,0) mg/m3 (0,02 – 5,0) mg in the sample selenium (0,005 – 0,7) mg/m3 (0,007 – 1,0) mg in the sample silver (0,005 – 0,5) mg/m3 (0,003 – 0,5) mg in the sample potassium hydroxide (0,005 – 5,0) mg/m3 (0,0072 – 7,15) mg in the sample sodium hydroxide (0,005 – 5,0) mg/m3 (0,0100 – 10,0) mg in the sample iron (0,005 – 5,0) mg/m3 (0,005 – 5,0) mg in the sample |
Flame atomic absorption spectrometry (FAAS) characteristics/method | PB-04 issue 5 of 01.07.2019 | |
| 281 | Waste gases | Concentration/Content of chromium (VI) Range (0,0011 – 0,50) mg/m3 Range (0,0022 – 0,22) mg in the sample |
Spectrophotometric method | PB-06 issue 3 of 01.07.2019 | |
| 282 | Waste gases | Sampling for determination of formaldehyde concentration | Aspiration method using absorbing solutions | PB-09 issue 18 of 10.10.2024 | |
| 283 | Waste gases | Formaldehyde emission (calculated) | PB-09 issue 18 of 10.10.2024 | ||
| 284 | Waste gases | Sampling for determination of formaldehyde concentration | Aspiration method using sorption tubes | PB-09 issue 18 of 10.10.2024 | |
| 285 | Waste gases | Formaldehyde emission (calculated) | PB-09 issue 18 of 10.10.2024 | ||
| 286 | Waste gases | Sampling for determination of ammonia concentration | Aspiration method using absorbing solutions | PN-EN ISO 21877:2020-03 | |
| 287 | Waste gases | Concentration/Content of ammonia Range (0,1 – 200) mg/m3 Range (0,00335 – 15) mg in the sample |
Spectrophotometric method | PN-EN ISO 21877:2020-03 | |
| 288 | Waste gases | Ammonia emission (calculated) | PN-EN ISO 21877:2020-03 | ||
| 289 | Waste gases | Formaldehyde concentration/content Range (0,1 – 20) mg/m3 Range (0,002 – 0,4) mg in the sample |
Spectrophotometric method | PB-12 issue 5 of 01.07.2019 | |
| 290 | Waste gases | Concentration/Content of chlorine Range (0,06 – 2,6) mg/m3 Range (0,001 – 0,04) mg in the sample |
Spectrophotometric method | PB-16 issue 1 of 05.05.2020 | |
| 291 | Waste gases | Sampling of sulfuric acid and sulfur trioxide | Aspiration method using membrane filters | PB-09 issue 18 of 10.10.2024 | |
| 292 | Waste gases | Concentration/Content sulphuric(VI) acid Range (0,1 – 33,0) mg/m3 Range (0,1 – 10,0) mg in the sample sulphur trioxide Range (0,08 – 27,4) mg/m3 Range (0,08 – 8,3) mg in the sample |
Turbidimetric method | PB-11 issue 5 of 01.07.2019 | |
| 293 | Waste gases | Sulfuric acid emission (calculated) | PB-09 issue 18 of 10.10.2024 | ||
| 294 | Waste gases | Emission of sulphur trioxide (calculated) | PB-09 issue 18 of 10.10.2024 | ||
| 295 | Waste gases | Sampling for the determination of chlorine concentration | PB-09 issue 18 of 10.10.2024 | ||
| 296 | Waste gases | Chlorine emission (calculated) | PB-09 issue 18 of 10.10.2024 | ||
| 297 | Waste gases | Sampling for determination of acetic acid concentration | PB-09 issue 18 of 10.10.2024 | ||
| 298 | Waste gases | Emission of acetic acid (calculated) characteristics/method | PB-09 issue 18 of 10.10.2024 | ||
| 299 | Waste gases | Sampling for the determination of ozone concentration | PB-09 issue 18 of 10.10.2024 | ||
| 300 | Waste gases | Ozone emission (calculated) | PB-09 issue 18 of 10.10.2024 | ||
| 301 | Waste gases | Sampling for the determination of fluorine concentration | ISO 15713:2006 | PB-09 issue 18 of 10.10.2024 | ||
| 302 | Waste gases | Fluorine emission (calculated) | ISO 15713:2006 | PB-09 issue 18 of 10.10.2024 | ||
| 303 | Waste gases | Concentration/Content gaseous fluorides expressed as hydrogen fluoride Range (0,04 – 219) mg/m3 Range (0,0053 – 10,5) mg in the sample hydrogen fluoride Range (0,04 – 219) mg/m3 Range (0,0053 – 10,5) mg in the sample fluorine Range (0,04 – 170) mg/m3 Range (0,005 – 10) mg in the sample |
Potentiometric method | ISO 15713:2006 | |
| 304 | Waste gases | Sampling for determination of hydrogen sulphide concentration | PB-09 issue 18 of 10.10.2024 | ||
| 305 | Waste gases | Hydrogen sulphide emission (calculated) | PB-09 issue 18 of 10.10.2024 | ||
| 306 | Waste gases | Concentration/Content of hydrogen sulfide Range (0,7 – 160,0) mg/m3 Range (0,01 – 16,0) mg in the sample |
Spectrophotometric method | PB-10 issue 2 of 01.07.2019 | |
| 307 | Waste gases | Concentration/Content: phenol Range (0,08 – 5000) mg/m3 Range (0,0050 – 13,64) mg in the sample cresol (mixture of isomers) (0,17 – 2000) mg/m3 (0,01 – 15,2) mg in the sample |
Gas chromatography with flame ionization detection (GC-FID) | PB-02 issue 12 of 16.10.2023 | |
| 308 | Waste gases | Concentration/Content of acetic acid Range (0,83 – 667) mg/m3 Range (0,05 – 20) mg in the sample |
Gas chromatography with flame ionization detection (GC-FID) characteristics/method | PB-02 issue 12 of 16.10.2023 | |
| 309 | Waste gases | Sampling for determination of the concentrations of nitrogen oxide, nitrogen dioxide, nitric acid, sulfur dioxide | PB-09 issue 18 of 10.10.2024 | ||
| 310 | Waste gases | Emission of nitrogen monoxide, nitrogen dioxide, nitric acid, sulphur dioxide (calculated) | PB-09 issue 18 of 10.10.2024 | ||
| 311 | Waste gases | Concentration/Content of nitrogen monoxide Range (0,032 – 50) mg/m3 Range (0,00065 – 0,1) mg in the sample |
Spectrophotometric method | PN-90/Z-04009/05 | |
| 312 | Waste gases | Concentration/Content of nitrogen dioxide Range (0,050 – 78) mg/m3 Range (0,001 – 0,156) mg in the sample |
Spectrophotometric method | PN-90/Z-04009/05 | |
| 313 | Waste gases | Concentration/Content of nitric (V) acid Range (0,068 – 107) mg/m3 Range (0,0014 – 0,214) mg in the sample |
Spectrophotometric method | PN-90/Z-04009/05 | |
| 314 | Waste gases | Concentration/Content of sulphur dioxide Range (0,16 – 32) mg/m3 Range (0,0032 – 0,64) mg in the sample |
Spectrophotometric method | PB-08 issue 2 of 01.07.2019 | |
| 315 | Waste gases | O2, SO2, NO concentration O2 (0,54 – 21,0) % SO2 (14 – 2600) mg/m3 NO (4,0 – 1200) mg/m3 |
Electrochemical method | PN-ISO 10396:2001 | |
| 316 | Waste gases | Emission of O2, SO2, NO (calculated) | PN-ISO 10396:2001 | ||
| 317 | Waste gases | Sampling for the determination of PAH concentration | ISO 11338-1:2003 – Method B | ISO 11338-2:2003 | ||
| 318 | Waste gases | PAH emission (calculated) | ISO 11338-1:2003 – Method B | ISO 11338-2:2003 | ||
| 319 | Waste gases | Sampling for determination of pentane concentration | PB-09 issue 18 of 10.10.2024 | ||
| 320 | Waste gases | Emission of pentane (calculated) | PB-09 issue 18 of 10.10.2024 | ||
| 321 | Waste gases | Sampling for determination of propan-1-ol concentration | PB-09 issue 18 of 10.10.2024 | ||
| 322 | Waste gases | Emission of propan-1-ol (calculated) | PB-09 issue 18 of 10.10.2024 | ||
| 323 | Waste gases | Sampling for determination of the mass concentration of dioxin-like PCBs | PN-EN 1948-4+A1:2014-03 | ||
| 324 | Waste gases | Emission of PCB (calculated) characteristics/method | PN-EN 1948-4+A1:2014-03 | ||
| 325 | Waste gases | Concentration/Content polycyclic hydrocarbons aromatic (PAH) naphthalene filters (0,00002 – 1,000) mg/m3 Range (0,03 – 24) μg in the sample tubes (0,00002 – 1,000) mg/m3 (0,02 – 24) μg in the sample acenaphthene filters (0,00002 – 1,000) mg/m3 (0,02– 23) μg in the sample tubes (0,00003 – 1,000) mg/m3 (0,03 – 25) μg in the sample fluorene filters (0,00001 – 1,000) mg/m3 (0,01 – 23) μg in sample tubes (0,00001 – 1,000) mg/m3 (0,01 – 23) μg in sample phenanthrene filters (0,00002 – 1,000) mg/m3 (0,02 – 23) μg in the sample tubes (0,00002 – 1,000) mg/m3 (0,02 – 22) μg in sample anthracene filters (0,00001 – 1,000) mg/m3 (0,01 – 23) μg in sample tubes (0,00001 – 1,000) mg/m3 (0,01 – 23) μg in sample fluoranthene filters (0,00002 – 1,000) mg/m3 (0,02 – 23) μg in the sample tubes (0,00002 – 1,000) mg/m3 (0,02 – 23) μg in sample pyrene filters (0,00002 – 1,000) mg/m3 (0,02 – 23) μg in the sample tubes (0,00002 – 1,000) mg/m3 (0,02 – 24) μg in the sample benzo(a)anthracene filters (0,00002 – 1,000) mg/m3 (0,02 – 22) μg in the sample tubes (0,00002 – 1,000) mg/m3 (0,02 – 23) μg in the sample |
High-performance liquid chromatography with fluorescence detection (HPLC-FLD) acenaphthylene - filters (0,00002 – 1,000) mg/m3 (0,02 – 23) μg in the sample - tubes (0,00002 – 1,000) mg/m3 (0,02 – 22) μg in the sample; High-performance liquid chromatography with ultraviolet detection (HPLC-UV) characteristics/method | ISO 11338-2:2003 | |
| 326 | Waste gases | Concentration/Content polycyclic hydrocarbons aromatic (PAH) chrysene filters (0,00001 – 1,000) mg/m3 Range (0,01 – 23) μg in sample tubes (0,00001 – 1,000) mg/m3 (0,01 – 23) μg in sample benzo(b)fluoranthene filters (0,00002 – 1,000) mg/m3 (0,02 – 23) μg in the sample tubes (0,00002 – 1,000) mg/m3 (0,02 – 23) μg in sample benzo(k)fluoranthene filters (0,00002 – 1,000) mg/m3 (0,02 – 22) μg in the sample tubes (0,00002 – 1,000) mg/m3 (0,02 – 24) μg in the sample dibenzo(a,h)anthracene filters (0,00002 – 1,000) mg/m3 (0,02 – 22) μg in the sample tubes (0,00002 – 1,000) mg/m3 (0,02 – 24) μg in the sample benzo(g,h,i)perylene filters (0,00002 – 1,000) mg/m3 (0,02 – 22) μg in the sample tubes (0,00003 – 1,000) mg/m3 (0,03 – 27) μg in the sample indeno (1,2,3-cd)pyrene filters (0,00002 – 1,000) mg/m3 (0,02 – 22) μg in the sample tubes (0,00003 – 1,000) mg/m3 (0,03 – 26) μg in the sample benzo(a)pyrene filters (0,00001 – 1,000) mg/m3 (0,01 – 22) μg in the sample tubes (0,00001 – 1,000) mg/m3 (0,01 – 25) μg in the sample |
High-performance liquid chromatography with fluorescence detection (HPLC-FLD) | ISO 11338-2:2003 | |
| 327 | Sum of polycyclic aromatic hydrocarbons (calculated) | Sum of polycyclic aromatic hydrocarbons (calculated) characteristics/method | ISO 11338-2:2003 | ||
| 328 | Waste gases | Concentration/Content | PB-17 issue 2 of 26.11.2021 | PB-17 | ||
| 329 | Waste gases | methylenebis(phenyl isocyanate) (4,4-methylenebis(phenyl isocyanate); |
issue 2 of 26.11.2021 | ||
| 330 | Waste gases | MDI) Range (0,0003 – 0,28) mg/m3 Range (0,05 – 50) μg in the sample toluene-2,4-diyl diisocyanate (toluene 2,4-diisocyanate); 2,4-TDI) Range (0,0003 – 0,28) mg/m3 Range (0,05 – 50) μg in the sample toluene-2,6-diyl diisocyanate (toluene 2,6-diisocyanate; 2,6-TDI) Range (0,0003 – 0,28) mg/m3 Range (0,05 – 50) μg in the sample hexane-1,6-diyl diisocyanate, (hexamethylene 1,6-diisocyanate; 1,6-HDI) Range (0,0005 – 0,28) mg/m3 Range (0,10 – 50) μg in the sample |
High-performance liquid chromatography with fluorescence detection (HPLC-FLD) | issue 2 of 26.11.2021 | |
| 331 | Waste gases | Formaldehyde concentration/content | PB-18 issue 2 of 20.09.2024 | PB-18 | ||
| 332 | Waste gases | Range (0,0034 – 40) mg/m3 Range (0,0001 – 0,1) mg in the sample |
High-performance liquid chromatography with spectrophotometric detection (HPLC-UV) | issue 2 of 20.09.2024 | |
| 333 | Waste gases | Sampling for determination of | PB-09 issue 18 of 10.10.2024 | PB-09 | ||
| 334 | Waste gases | concentrations of acrylaldehyde (acrolein) | Aspiration method using sorption tubes | issue 18 of 10.10.2024 | |
| 335 | Waste gases | Emission of acrylaldehyde (acrolein) (calculated) | issue 18 of 10.10.2024 | ||
| 336 | Waste gases | Concentration/Content of acrylaldehyde | PB-18 issue 2 of 20.09.2024 | PB-18 | ||
| 337 | Waste gases | Range (0,0017 – 20) mg/m Range (0,00005 – 0,04) mg in the sample |
High-performance liquid chromatography with spectrophotometric detection (HPLC-UV) | issue 2 of 20.09.2024 | |
| 338 | Landfill gas/Biogas | O2 concentration | PB-15 issue 4 of 07.02.2022 | PB-15 | ||
| 339 | Landfill gas/Biogas | Range (0,6 – 21) % |
Electrochemical method | issue 4 of 07.02.2022 | |
| 340 | Landfill gas/Biogas | CO2, CH4 concentration | issue 4 of 07.02.2022 | ||
| 341 | Landfill gas/Biogas | CO2 (0,3 – 50) % | issue 4 of 07.02.2022 | ||
| 342 | Landfill gas/Biogas | CH4 (0,3 – 75) % | Non-dispersive infrared spectrometry (NDIR) | issue 4 of 07.02.2022 | |
| 343 | Landfill gas/Biogas | Emission of CO2, CH4 (calculated) | issue 4 of 07.02.2022 | ||
| 344 | Landfill gas/Biogas | Flow velocity Range (0,5 – 20) m/s |
Anemometric method | issue 4 of 07.02.2022 | |
Reference standards (145)
11/33
ISO 11338-1:2003 – Method B
ISO 11338-2:2003
ISO 12039:2019
ISO 15713:2006
Issue 1, dated 15 January 1998
NIOSH Method 1302,
NIOSH Method 1302, Issue 1, dated 15 January 1998
NIOSH Method 7600, Issue 3, dated 20 October 2015
NIOSH Method 7902 Issue 2, dated 15 August 1994
PB-01 issue 13 of 14.10.2024
PB-02
PB-02 issue 12 of 16.10.2023
PB-03 issue 9 of 24.01.2024
PB-04 issue 5 of 01.07.2019
PB-05 issue 4 of 03.12.2024
PB-06 issue 3 of 01.07.2019
PB-08 issue 2 of 01.07.2019
PB-09
PB-09 issue 18 of 10.10.2024
PB-10 issue 2 of 01.07.2019
PB-11 issue 5 of 01.07.2019
PB-12 issue 5 of 01.07.2019
PB-14 issue 5 of 14.01.2022
PB-15
PB-15 issue 4 of 07.02.2022
PB-16 issue 1 of 05.05.2020
PB-17
PB-17 issue 2 of 26.11.2021
PB-18
PB-18 issue 2 of 20.09.2024
PN-71/Z-04041
PN-75/Z-04037/03
PN-76/Z-04045/02
PN-78/Z-04047/02
PN-78/Z-04118/01
PN-79/Z-04081/01
PN-79/Z-04106/02
PN-79/Z-04107/02
PN-81/Z-04134/02
PN-81/Z-04134/03
PN-83/E-04040.03
PN-84/Z-04137/02
PN-84/Z-04138/02
PN-86/Z-04151/02
PN-86/Z-04152/02
PN-86/Z-04165/02
PN-86/Z-04166/02
PN-87/B-02156
PN-87/Z-04100/03
PN-87/Z-04178/02
PN-88/Z-04187/02
PN-90/Z-04009/05
PN-90/Z-04079/10
PN-92/Z-04113/09
PN-92/Z-04227/02
PN-93/Z-04225/03
PN-EN 12599:2013
PN-EN 12619:2013-05
PN-EN 13211+AC:2006
PN-EN 13284-1:2018-02
PN-EN 13649:2005
PN-EN 14253+A1:2011
PN-EN 14385:2005
PN-EN 14789:2017-04
PN-EN 14790:2017-04
PN-EN 14791:2017-04
PN-EN 14792:2017-04
PN-EN 1911:2011
PN-EN 1948-1:2006+Ap1:2017-08
PN-EN 1948-4+A1:2014-03
PN-EN ISO 11079:2008
PN-EN ISO 21877:2020-03
PN-EN ISO 23210:2010
PN-EN ISO 3746:2011/Ap1:2017-09 excluding cl. 8.4.
PN-EN ISO 5349-1:2004
PN-EN ISO 5349-2:2004
PN-EN ISO 5349-2:2004/A1:2015
PN-EN ISO 7243:2018-01
PN-EN ISO 7730:2006
PN-EN ISO 7730:2006/Ap2:2016
PN-EN ISO 9612:2011 excluding the method covering strategy 3 - cl. 11
PN-G-02600:1996 cl. 3
PN-G-02601:1999 cl. 3
PN-ISO 10396:2001
PN-ISO 15058:2017-04
PN-ISO 9613-2:2002
PN-M-34129:1987 – Method A
PN-N-01307:1994
PN-Z-01339:2020-12
PN-Z-04008-7:2002+Az1:2004
PN-Z-04009-11:2008
PN-Z-04015-12:1996
PN-Z-04015-13:1996
PN-Z-04016-10:2005
PN-Z-04016-4:1998
PN-Z-04016-6:1998
PN-Z-04030-7:1994
PN-Z-04045-16:2010
PN-Z-04073-1:2014-08
PN-Z-04102-3:2013-10
PN-Z-04108-5:2006
PN-Z-04119-10:2008
PN-Z-04136-3:2003
PN-Z-04146-3:2006
PN-Z-04216-2:2012
PN-Z-04224-3:2003
PN-Z-04240-2:1999
PN-Z-04240-4:1999
PN-Z-04240-5:2006
PN-Z-04263-1:2012
PN-Z-04304:2003
PN-Z-04318:2005
PN-Z-04323:2004
PN-Z-04354:2005
PN-Z-04379:2010
PN-Z-04399:2011
PN-Z-04434:2011
PN-Z-04435:2011
PN-Z-04436:2011
PN-Z-04437:2011
PN-Z-04450:2014
PN-Z-04468:2015-10
PN-Z-04469:2025-02
PN-Z-04472:2015
PN-Z-04476:2016
PN-Z-04478:2016-10
PN-Z-04487:2017-10
PN-Z-04488:2017-10
PN-Z-04490:2017
PN-Z-04507:2022-05
PN-Z-04507:2022-05/Ap1:2022-08
PN-Z-04508:2022-05
PN-Z-04508:2022-05/Ap1:2022-08
PN-Z-04535:2022-01
PiMOŚP 1999, No. 22, pp. 96-100
PiMOŚP 2012, No. 4(74) pp. 117-130
PiMOŚP 2021, No. 4(110), pp. 179-189
Annex 7 to the Regulation of the Minister of Climate and Environment of 07.09.2021 (consolidated text Journal of Laws 2023 item 1706)
Annex 3 to the Regulation of the Minister of the Environment of 16 June 2011 (Journal of Laws 2011 No. 140 item 824) (Journal of Laws 2011 No. 288 item 1697) excluding cl. H
issue 12 of 16.10.2023
issue 18 of 10.10.2024
issue 2 of 20.09.2024
issue 2 of 26.11.2021
issue 4 of 07.02.2022