Difference between revisions of "Air Sampling"
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− | + | This article serves two purposes. | |
− | |||
− | |||
− | = Charcoal Tubes = | + | First, it provides descriptions of the more straightforward air sampling concepts and procedures. |
− | ''<small>From | + | |
− | * | + | Second, if an air sampling method involves more details such that it needs its own article, this page will act as a hub for those additional methods. |
+ | |||
+ | '''''One thing to remember:''''' A large amount of this information came from, and can be found in, the [[OSHA Technical Manual]] (OTM) [https://www.osha.gov/dts/osta/otm/otm_ii/otm_ii_1.html Section II Chapter 1]. Certain sections of the OTM were updated as recently as at least 2014, including this chapter on air sampling. | ||
+ | |||
+ | == Arrangements of Sampling Train == | ||
+ | '''''TO DO''': Explain, with pictures, the sampling train for regular setups and, especially, low-flow setups.'' | ||
+ | |||
+ | == Carbon Monoxide (CO) == | ||
+ | Carbon monoxide is sampled with the [[ToxiRAE Pro]]. Refer to its article for information on sampling for CO. | ||
+ | * Use Form [[Forms#OSHA-93 Direct Reading Report|OSHA-93 Direct Reading Report]]. | ||
+ | * CO has an IDLH of 1200 ppm. | ||
+ | |||
+ | == Charcoal Tubes == | ||
+ | [[File:Charcoal_tube_diagram.png|thumb|Charcoal Tube Diagram|297x297px]]''<small>From https://www.skcinc.com/catalog/product_info.php?products_id=567</small>'' | ||
+ | *Just before sampling, use a scorer/breaker tool to uniformly break the ends of the sorbent tube to a 2 mm diameter or '''''half the diameter of the tube body'''''. | ||
* Keep the tube in a vertical position during sampling to prevent the possibility of '''channeling''' that can lead to under-sampling. | * Keep the tube in a vertical position during sampling to prevent the possibility of '''channeling''' that can lead to under-sampling. | ||
* The arrow on the tube indicates air flow direction and should '''point to the tube holder and pump'''. If no arrow is present, the smallest section should be near the tube holder. | * The arrow on the tube indicates air flow direction and should '''point to the tube holder and pump'''. If no arrow is present, the smallest section should be near the tube holder. | ||
− | = Impinger = | + | == Impinger == |
+ | The impinger is used when no solid medium is available to "catch" the analyte and must, therefore, be dissolved in a liquid medium. The air from the work environment is passed (as bubbles) ''through'' the liquid medium at a rate slow enough to allow the analyte to dissolve and/or react with the medium. | ||
+ | |||
+ | Because a liquid medium is involved, much more consideration must be put into placing this on the employee or in the work area. In some cases, the liquid medium is a corrosive acid. Furthermore, the impinger is made of glass. It is recommended to '''watch the employee''' as much and as closely as possible to ensure nothing the employee does will endanger the impinger, its contents, and, ultimately, the employee. | ||
+ | |||
[http://youtu.be/Ob9vrfje_YQ Video] demonstrating setup and usage. | [http://youtu.be/Ob9vrfje_YQ Video] demonstrating setup and usage. | ||
+ | {{#ev:youtube|Ob9vrfje_YQ}} | ||
− | = Isocyanates = | + | == Isocyanates == |
− | Enter Isocyanate sampling methods and info about solvent stability. | + | '''''TO DO:''' Enter Isocyanate sampling methods and info about solvent stability.'' |
− | = | + | == Low Flow Sampling == |
+ | ''Visit the [[Low Flow Sampling]] page for information.'' | ||
− | == Method == | + | == Mold Sampling == |
− | {| | + | |
− | + | === Method === | |
+ | {| class="wikitable" | ||
+ | !Time | ||
|2 Hours | |2 Hours | ||
|- | |- | ||
− | + | !Media | |
− | |MCEF in | + | |MCEF in 37mm filter cassette |
|- | |- | ||
− | + | !Flow Rate | |
|2 L/min | |2 L/min | ||
|- | |- | ||
− | + | !Tubing | |
− | |Use a short length of tubing — just long enough to be able to flex | + | |Use a short length of tubing — just long enough to be able to flex so the cassette inlet points down. |
|} | |} | ||
− | * The intake on the cassette | + | * The intake on the cassette needs to always be facing down so that other, heavier particles will not land on the filter. |
− | * One pump is used '''outside''' | + | * One pump is used '''outside''' to get the CFU count for the facility's surrounding environment. |
+ | * One ''or more'' pumps are placed '''inside''' around the areas of concern. | ||
− | == Notes == | + | === Notes === |
− | * When results come back with a significantly higher fungus count (CFU/m³) for the inside as opposed to the outside count, a letter is sent to the company contact detailing the findings, the hazards, and remediation. | + | * When results come back with a significantly higher fungus count (CFU/m³) for the inside as opposed to the outside count, a letter is sent to the company contact detailing the findings, the hazards, and remediation. Click [https://s3oshkynet.s3.amazonaws.com/Forms/Mold%20Letter.docx here] to download the letter template. |
− | ** The letter is printed out and submitted in the report under the IB tab. | + | ** The CSHO compiles a draft letter, which is printed out and submitted in the report under the IB tab. |
− | ** The digital original is sent to your supervisor so that it can be passed on to | + | ** The digital original is sent to your supervisor so that it can be passed on to an admin for revising the date and for review by the Program Manager. |
− | |||
− | = Respirable Dust – Cyclone = | + | === Total Spore Counts vs. Colony Forming Units (CFU) === |
+ | ''From "[http://www.emsl.com/index.cfm?nav=Pages&ID=116 Smells moldy in here]" - EMSL.com''<blockquote>Air sampling methods can be divided into two different categories: methods generating <span style="background:#d5fdf4">“total spore counts,” typically reported as counts per cubic meter (m³)</span> and methods that determine <span style="background:#fee7e6">“culturable fungi,” typically reported as colony forming units (CFU) per cubic meter</span>. <span style="background:#d5fdf4">Total spores counts are an amalgamate of both living and nonliving spores. These methods do not allow for the discrimination between living or dead spores</span>. <span style="background:#fee7e6">Culturable fungi results, tabulate only living fungal particles, which can include hyphal fragments as well as spores</span>.</blockquote><blockquote>Sampling for total spore counts can be carried out using specially-greased slides and a Burkard or Allergenco sampler. Initial costs for these devices are high but subsequent purchases of greased slides are relatively inexpensive. The principal behind each of these devices is the same; air is vacuumed through and condensed onto the greased slide. Particles in the air are forced onto the grease, become embedded, and stick to its surface.</blockquote><blockquote>A more common approach would be to use your own vacuum pump with specially-designed, single-use spore-trap cassettes. Some of the popular cassettes on the market include the Cyclex-d, Air-O-Cell, Microcell5, and the Laro100. Particles in the air are trapped in the cassette either on a proprietary adhesive or, as in the case of the Laro100, a 0.8-micron (mm) filter. The cassettes are opened, prepped and examined under a microscope in a laboratory by properly trained analysts who determine the total spore count. <span style="background:#98FB98">Depending upon your specific complaint or scenario, it ''may not'' be important to know the ''viability'' of a spore, since dead spores are also potentially allergenic or toxigenic to susceptible individuals</span>.</blockquote> | ||
+ | |||
+ | == Nitrogen Dioxide (NO<sub>2</sub>) == | ||
+ | Nitrogen dioxide is sampled with the [[ToxiRAE Pro]]. Refer to its article for information on sampling for NO₂. | ||
+ | * Use Form [[Forms#OSHA-93 Direct Reading Report|OSHA-93 Direct Reading Report]]. | ||
+ | * NO<sub>2</sub> has an IDLH of 20 ppm. | ||
+ | |||
+ | == Respirable Dust – Cyclone == | ||
+ | [[File:Place Holder Image.png|thumb|Dorr-Oliver Cycone in an MSA Sampling Train|297x297px]] | ||
{| class="wikitable" | {| class="wikitable" | ||
+ | |- | ||
!Media | !Media | ||
− | + | |PVC (pre-weighed) in '''two-piece''' 37mm filter cassette | |
− | |||
− | |||
|- | |- | ||
− | + | !Flow Rate | |
− | + | |1.7 L/min | |
− | |||
− | | | ||
|- | |- | ||
− | + | !Volume | |
− | + | |Minimum: | |
− | | | + | Maximum: |
− | |||
|- | |- | ||
− | + | !Calibration | |
− | + | |''Refer to the [[Calibration]] page'' | |
− | |||
− | | | ||
|} | |} | ||
− | |||
− | |||
− | |||
− | = | + | === Notes === |
− | * | + | * Using a Cyclone eliminates all particles but '''respirable''' particles. |
+ | * '''Respirable particles''' are those particles in the size range which would be deposited in the gas exchange region of the lung. Particles too large to be inhaled are collected in a grit pot on the cyclone. The respirable fraction is captured on a pre-weighed PVC filter for ''gravimetric'' analysis. | ||
+ | * [https://www.osha.gov/dts/osta/otm/otm_ii/otm_ii_1.html#appendix_II_2 Appendix B] to OTM Section II: Chapter 1 lists dusts for which respirable sampling should be performed. | ||
− | * | + | == Screening == |
− | * | + | There are several methods KYOSH uses to screen for substances. These include: |
+ | * [[Check Swabs]] | ||
+ | * [[Draeger|Dräger]] CHIPs | ||
+ | * Quest Sound Level Meters and 3M Edge Noise Dosimeters | ||
+ | * [[ToxiRAE Pro]] | ||
+ | * [[Multi-Gas Monitors|RKI Multi-Gas Monitors]] | ||
+ | * [[SAPPHIRE]] Portable Gas Detector | ||
+ | When screening for substances with a direct read device, results are recorded on an [[Forms#OSHA-93 Direct Reading Report|OSHA-93 Direct Reading Report]] form, which details each location screened and results. | ||
− | + | Additionally, an [[Forms#OSHA-98 Screening Report|OSHA-98 Screening Report]] form should be completed for all screened substances. | |
+ | |||
+ | <nowiki>[Why both of them? I don't know why, but that's what DM says. :) ]</nowiki> | ||
+ | |||
+ | == Welding & Arc Cutting Fumes == | ||
+ | [[File:Welding Helmet Adapter.jpg|thumb|Welding Helmet Adapter Tubing]] | ||
{| class="wikitable" | {| class="wikitable" | ||
− | |||
− | |||
− | |||
− | |||
− | |||
− | |||
|- | |- | ||
− | | | + | !Media |
− | | | + | |MCEF |
− | | | + | * 25 mm filter cassette if wearing welding helmet |
− | | | + | * 37 mm filter cassette otherwise |
− | | | + | |- |
− | + | !Flow Rate | |
+ | |2 L/min | ||
+ | |- | ||
+ | !Volume | ||
+ | |Minimum: 480 L | ||
+ | Maximum: 960 L | ||
|- | |- | ||
− | + | !Tubing | |
− | + | |Helmet Adapter (''Refer to image'') | |
− | |||
− | |||
− | |||
− | | | ||
|} | |} | ||
− | |||
− | + | === Notes === | |
+ | The ''usual'' purpose for sampling welding and arc cutting fumes is the determination of exposure to metal fumes. Most metals have PELs for the element itself. However, there are '''two metals''' which have a PEL not for the element but for an ''oxide'' of the metal: | ||
+ | * '''iron''', as trivalent iron Fe(III) in Fe₂O₃; and | ||
+ | * '''zinc''', as divalent zinc Zn(II) in ZnO. | ||
+ | Furthermore, there are some metals that have expanded standards, such as [[lead]] and [[Hexavalent Chromium|hexavalent chromium]] — Cr(VI). Refer to their specific pages for sampling guidelines. Please note that, in the case of sampling for fumes of chromium, all valences of chromium will be detected using this method — Cr(II), Cr(III), and Cr(VI). There is no way to use this method to single out the individual valences. | ||
− | + | '''Manganese''' is only limited by a Ceiling value. As far as compliance goes, there is no need to calculate the TWA. However, to be thorough, there is no harm in calculating the TWA and including it in your report but not on your OSHA-91(S) result lines. | |
− | = | + | == Article To-Dos == |
− | * | + | * Add Sampling Method numbers and links to each of the tables. |
− | + | [[Category:Sampling]] |
Latest revision as of 15:05, 28 September 2018
This article serves two purposes.
First, it provides descriptions of the more straightforward air sampling concepts and procedures.
Second, if an air sampling method involves more details such that it needs its own article, this page will act as a hub for those additional methods.
One thing to remember: A large amount of this information came from, and can be found in, the OSHA Technical Manual (OTM) Section II Chapter 1. Certain sections of the OTM were updated as recently as at least 2014, including this chapter on air sampling.
Arrangements of Sampling Train
TO DO: Explain, with pictures, the sampling train for regular setups and, especially, low-flow setups.
Carbon Monoxide (CO)
Carbon monoxide is sampled with the ToxiRAE Pro. Refer to its article for information on sampling for CO.
- Use Form OSHA-93 Direct Reading Report.
- CO has an IDLH of 1200 ppm.
Charcoal Tubes
From https://www.skcinc.com/catalog/product_info.php?products_id=567
- Just before sampling, use a scorer/breaker tool to uniformly break the ends of the sorbent tube to a 2 mm diameter or half the diameter of the tube body.
- Keep the tube in a vertical position during sampling to prevent the possibility of channeling that can lead to under-sampling.
- The arrow on the tube indicates air flow direction and should point to the tube holder and pump. If no arrow is present, the smallest section should be near the tube holder.
Impinger
The impinger is used when no solid medium is available to "catch" the analyte and must, therefore, be dissolved in a liquid medium. The air from the work environment is passed (as bubbles) through the liquid medium at a rate slow enough to allow the analyte to dissolve and/or react with the medium.
Because a liquid medium is involved, much more consideration must be put into placing this on the employee or in the work area. In some cases, the liquid medium is a corrosive acid. Furthermore, the impinger is made of glass. It is recommended to watch the employee as much and as closely as possible to ensure nothing the employee does will endanger the impinger, its contents, and, ultimately, the employee.
Video demonstrating setup and usage.
Isocyanates
TO DO: Enter Isocyanate sampling methods and info about solvent stability.
Low Flow Sampling
Visit the Low Flow Sampling page for information.
Mold Sampling
Method
Time | 2 Hours |
---|---|
Media | MCEF in 37mm filter cassette |
Flow Rate | 2 L/min |
Tubing | Use a short length of tubing — just long enough to be able to flex so the cassette inlet points down. |
- The intake on the cassette needs to always be facing down so that other, heavier particles will not land on the filter.
- One pump is used outside to get the CFU count for the facility's surrounding environment.
- One or more pumps are placed inside around the areas of concern.
Notes
- When results come back with a significantly higher fungus count (CFU/m³) for the inside as opposed to the outside count, a letter is sent to the company contact detailing the findings, the hazards, and remediation. Click here to download the letter template.
- The CSHO compiles a draft letter, which is printed out and submitted in the report under the IB tab.
- The digital original is sent to your supervisor so that it can be passed on to an admin for revising the date and for review by the Program Manager.
Total Spore Counts vs. Colony Forming Units (CFU)
From "Smells moldy in here" - EMSL.com
Air sampling methods can be divided into two different categories: methods generating “total spore counts,” typically reported as counts per cubic meter (m³) and methods that determine “culturable fungi,” typically reported as colony forming units (CFU) per cubic meter. Total spores counts are an amalgamate of both living and nonliving spores. These methods do not allow for the discrimination between living or dead spores. Culturable fungi results, tabulate only living fungal particles, which can include hyphal fragments as well as spores.
Sampling for total spore counts can be carried out using specially-greased slides and a Burkard or Allergenco sampler. Initial costs for these devices are high but subsequent purchases of greased slides are relatively inexpensive. The principal behind each of these devices is the same; air is vacuumed through and condensed onto the greased slide. Particles in the air are forced onto the grease, become embedded, and stick to its surface.
A more common approach would be to use your own vacuum pump with specially-designed, single-use spore-trap cassettes. Some of the popular cassettes on the market include the Cyclex-d, Air-O-Cell, Microcell5, and the Laro100. Particles in the air are trapped in the cassette either on a proprietary adhesive or, as in the case of the Laro100, a 0.8-micron (mm) filter. The cassettes are opened, prepped and examined under a microscope in a laboratory by properly trained analysts who determine the total spore count. Depending upon your specific complaint or scenario, it may not be important to know the viability of a spore, since dead spores are also potentially allergenic or toxigenic to susceptible individuals.
Nitrogen Dioxide (NO2)
Nitrogen dioxide is sampled with the ToxiRAE Pro. Refer to its article for information on sampling for NO₂.
- Use Form OSHA-93 Direct Reading Report.
- NO2 has an IDLH of 20 ppm.
Respirable Dust – Cyclone
Media | PVC (pre-weighed) in two-piece 37mm filter cassette |
---|---|
Flow Rate | 1.7 L/min |
Volume | Minimum:
Maximum: |
Calibration | Refer to the Calibration page |
Notes
- Using a Cyclone eliminates all particles but respirable particles.
- Respirable particles are those particles in the size range which would be deposited in the gas exchange region of the lung. Particles too large to be inhaled are collected in a grit pot on the cyclone. The respirable fraction is captured on a pre-weighed PVC filter for gravimetric analysis.
- Appendix B to OTM Section II: Chapter 1 lists dusts for which respirable sampling should be performed.
Screening
There are several methods KYOSH uses to screen for substances. These include:
- Check Swabs
- Dräger CHIPs
- Quest Sound Level Meters and 3M Edge Noise Dosimeters
- ToxiRAE Pro
- RKI Multi-Gas Monitors
- SAPPHIRE Portable Gas Detector
When screening for substances with a direct read device, results are recorded on an OSHA-93 Direct Reading Report form, which details each location screened and results.
Additionally, an OSHA-98 Screening Report form should be completed for all screened substances.
[Why both of them? I don't know why, but that's what DM says. :) ]
Welding & Arc Cutting Fumes
Media | MCEF
|
---|---|
Flow Rate | 2 L/min |
Volume | Minimum: 480 L
Maximum: 960 L |
Tubing | Helmet Adapter (Refer to image) |
Notes
The usual purpose for sampling welding and arc cutting fumes is the determination of exposure to metal fumes. Most metals have PELs for the element itself. However, there are two metals which have a PEL not for the element but for an oxide of the metal:
- iron, as trivalent iron Fe(III) in Fe₂O₃; and
- zinc, as divalent zinc Zn(II) in ZnO.
Furthermore, there are some metals that have expanded standards, such as lead and hexavalent chromium — Cr(VI). Refer to their specific pages for sampling guidelines. Please note that, in the case of sampling for fumes of chromium, all valences of chromium will be detected using this method — Cr(II), Cr(III), and Cr(VI). There is no way to use this method to single out the individual valences.
Manganese is only limited by a Ceiling value. As far as compliance goes, there is no need to calculate the TWA. However, to be thorough, there is no harm in calculating the TWA and including it in your report but not on your OSHA-91(S) result lines.
Article To-Dos
- Add Sampling Method numbers and links to each of the tables.