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The use of dustiness test for assessing
           exposures from asbestos in soils
                                  Garry Burdett* and Laurie Davies
                  Health and Safety Laboratory, Harpur Hill, Buxton SK17 9JN, UK.
                                      Garry.Burdett@hsl.gov.uk
•   Although the presence of asbestos in soil is
    a hazard, it will only pose a risk to workers
    and others, when it is made airborne and
    inhaled.
•   However, attempting to measure and
    assess the peak and cumulative airborne
    exposure of asbestos outdoors in the UK
    can be a frustrating and imprecise
    experience with UK weather conditions.
•   Wet weather surpresses dust release to air
    from on-site activity based sampling (e.g.
    as shown in use in the USA.)
•   An alternative solution is to simulate
    disturbance on “dry” samples using a
    standardised laboratory based, “Dustiness
    Tester” to measure the “realisibility” of
    asbestos fibres to air, from fragments of
    asbestos products and asbestos fibres in
    soils.
Re-design and calibration of the rotating drum
dustiness tester.
•   The calibration of the size selection
    was carried out using methods
    previously used to calibrate
    cyclones.
•   A TSI inc. Areodynamic Particle
    Sizer (APS) calibrated against a
    series of standard polystyrene
    spheres was used to calibrate for
    respirable (see figure), thoracic and
    PM10 fractions.
•   The respirable fraction was selected
    using coarse porous foams with an
    average pore diameters of 1920 µm,
    which minimised interception losses
    of fibres and changes to the fibre
    length distribution.
Results from ACM fragments recovered from
               waste land
•   Examples of results from ACM
    fragments recovered from waste
    land are given in figure 4
    standardised to a ~ 55 g test
    sample.

•   These results show order of
    magnitude variations between
    material types.

•   Results and are similar to peak
    workplace personal measurements
    with the same materials.
Results from soils with fine asbestos fibres:

•   Dispersions of fine asbestos fibres
    in soils have also been tested.

•   Dry soils can be very dusty so the
    sampling times were limited to two
    minutes to prevent overloading of
    the filter.

•   The worst-case situation for fibre
    release is shown, where crocidolite
    asbestos was dispersed for five
    minutes with an ultrasonic probe
    and mixed with a sandy soil matrix
    and then dried.
Conclusions

•   A modified rotating drum test based on
    EN 15051: 2006 has been developed
    which can be used to measure the
    release of respirable asbestos fibres to
    air from fragments of ACMs and soils.

•   The results from these tests can be used
    to support risk assessments and
    estimate the potential maximum peak
    emission levels to workers during dry
    periods.

•   Results from the test are helpful to
    surveyors, analysts and risk assessors
    for ranking and prioritising areas for
    management and remediation and
    checking the effectiveness of any clean-
    up, without waiting for the sun to shine.

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Garry Burdett - The use of dustiness test for assessing exposures from asbestos in soild

  • 1. The use of dustiness test for assessing exposures from asbestos in soils Garry Burdett* and Laurie Davies Health and Safety Laboratory, Harpur Hill, Buxton SK17 9JN, UK. Garry.Burdett@hsl.gov.uk • Although the presence of asbestos in soil is a hazard, it will only pose a risk to workers and others, when it is made airborne and inhaled. • However, attempting to measure and assess the peak and cumulative airborne exposure of asbestos outdoors in the UK can be a frustrating and imprecise experience with UK weather conditions. • Wet weather surpresses dust release to air from on-site activity based sampling (e.g. as shown in use in the USA.) • An alternative solution is to simulate disturbance on “dry” samples using a standardised laboratory based, “Dustiness Tester” to measure the “realisibility” of asbestos fibres to air, from fragments of asbestos products and asbestos fibres in soils.
  • 2. Re-design and calibration of the rotating drum dustiness tester. • The calibration of the size selection was carried out using methods previously used to calibrate cyclones. • A TSI inc. Areodynamic Particle Sizer (APS) calibrated against a series of standard polystyrene spheres was used to calibrate for respirable (see figure), thoracic and PM10 fractions. • The respirable fraction was selected using coarse porous foams with an average pore diameters of 1920 µm, which minimised interception losses of fibres and changes to the fibre length distribution.
  • 3. Results from ACM fragments recovered from waste land • Examples of results from ACM fragments recovered from waste land are given in figure 4 standardised to a ~ 55 g test sample. • These results show order of magnitude variations between material types. • Results and are similar to peak workplace personal measurements with the same materials.
  • 4. Results from soils with fine asbestos fibres: • Dispersions of fine asbestos fibres in soils have also been tested. • Dry soils can be very dusty so the sampling times were limited to two minutes to prevent overloading of the filter. • The worst-case situation for fibre release is shown, where crocidolite asbestos was dispersed for five minutes with an ultrasonic probe and mixed with a sandy soil matrix and then dried.
  • 5. Conclusions • A modified rotating drum test based on EN 15051: 2006 has been developed which can be used to measure the release of respirable asbestos fibres to air from fragments of ACMs and soils. • The results from these tests can be used to support risk assessments and estimate the potential maximum peak emission levels to workers during dry periods. • Results from the test are helpful to surveyors, analysts and risk assessors for ranking and prioritising areas for management and remediation and checking the effectiveness of any clean- up, without waiting for the sun to shine.