28 October 2015 Workplace exposure to airborne dust health effects amp risk quantification Gully Howard Technical Portsmouth In the UK there are 13000 deaths per year due to exposure to airborne hazardous substances at work ID: 537612
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HHSEG Topic Talk 28 October 2015Workplace exposure to airborne dust – health effects & risk quantification
Gully Howard Technical, PortsmouthSlide2
In the UK there are ~13,000 deaths per year due to exposure to airborne hazardous substances at work. Thousands of different chemical agents can potentially cause detrimental health effects in a wide range of different occupations. These airborne hazardous substances can be classified as either gases, vapours,
fibres, mists, fumes or dust.
Airborne hazardous substancesSlide3
Key Health Factors of DustsToxic effectWhat is the toxicology of the material and the respective target organ?Particle Size
Where does it deposit? – upper respiratory tract or is it capable of reaching the alveoli in the deep lung?Inhalable dust
(<100 microns) is the term given to all the dust capable of being inhaled through the nose and mouth.
Respirable
dust
(<10 microns) is the dust small enough to reach the gas exchange region of the deep lung.Slide4
Silica – worker exposure occurs in many industries affected e.g. mining, construction, ceramics
RCS – Silicosis (fibrosis of lung) can lead to lung cancer
Examples of hazardous dustsSlide5
Wood dust exposure occurs in the construction industry particularly in woodworking workshops
rhinitis, nose bleeds, asthma, nasal cancer
Examples of hazardous dustsSlide6
Diesel Particle Matter (DPM) some workers can potentially receive high exposures to DPM
IARC designated human carcinogen, EC, OC, TC
Examples of hazardous dustsSlide7
The COSHH Regulations provides guideline exposure levels for ‘non-hazardous dusts’ of 10 mg.m-3 inhalable dust and 4 mg.m-3 respirable dust.These levels for ‘non Hazardous’ dusts are
considered too high bymany (e.g. IOM suggest
controlling to 5 and 1 and
TUC 2.5 and 1 mg.m-3.)
‘Non-hazardous’ dustsSlide8
Breathing Zone
Personal samples MUST be taken in the Breathing Zone
300mm Hemisphere around the nose and mouth
Source :Airmet Scientific – reproduced with permissionSlide9
Sampling PumpsSmall battery powered pumps that can be worn by a person on a waist belt.Most particulate sampling is carried out at flow rate of either 2.0 or 2.2
litre/min.Slide10
IOM Sampling HeadGold standard sampling head for measuring inhalable dust fraction
All
collected dust measured
(filter
is weighed with the
cassette)
Easily handled
25 mm filter
2.0 litres/min (± 0.1)
IOM sampler
IOM cassette
Transport clip
Front Cassette Filter Support O ring Body
cover front grid
Source :Airmet Scientific-reproduced with permissionSlide11
Cyclone Sampling HeadRespirable dust
25/37 mm filter
2.2 litres/min (± 0.1)
Pump attached at top
Inlet points down
Source: HSE – reproduced with permissionSlide12
FiltersWide range of filter types including:
Glass
fibre
filters
Good particulate retention, collects at surface and within filter, best for gravimetric analysis
Mixed cellulose ester (MCE)
Weight easily affected by humidity changes
Easily dissolved for analysis (metals)
Particulates collected on surface only (transport)Slide13
Sample Train for Inhalable DustPumpConnecting tubeIOM sampling head
SAMPLER
CONNECTING
TUBE
PUMP
Source :Airmet Scientific – reproduced with permissionSlide14
Sampler worn by a workerSource :University of Wollongong
Pump usually placed on belt, in pocket or in suitable harness
Sample head in breathing zone
Calibrate flow rate at start
- note start time
Check flow rate during sampling
Check flow rate at end - note stop timeSlide15
Calibration of sampling system Connect from pump to sampling head Connect from sampling head to calibrator
Adjust flow to required flow rate
Source :Airmet Scientific – reproduced with permissionSlide16
Dust direct reading InstrumentsMost dust monitors are based on light scattering techniquesBeam of light shone through contaminated air. Light scattered by the dust is detected and is a measure of particulate concentrationSlide17
Deleading butt
Vacuuming butt and target area
Break period
Vacuuming and mopping rest of range
Cleaning surfaces in firing area with wipe cloth
Determining
pattern of exposure
Results
from a
direct-reading
dust instrument mounted on cleaner
Slide18
Observations and investigation‘Art of occupational hygiene’Determining exposure period - required for calculating time weighted average (TWA)Assessment of controls in place - this is not an optional extra – it is the law (Principles of good practice, Schedule 2A, COSHH Regs
)General feel of the workplace (i.e. culture) Slide19
Choosing a LabLab working to a Quality System (ISO 17025).Analytical methods are UKAS accredited.Take part in HSL’s Workplace Analysis Scheme for Proficiency
(WASP) for metals, BTEX, RCS etc and can show for the last 3 rounds that they are consistently close to the ‘true value’.Slide20
Occupational exposure limitsTime weight exposure (over 8 hrs or 15 mins) and compare with long or short term OELs.Legal limits in UK
WELs (EH40)
Other European country’s OELs –
IFA GESTIS
website
US ACGIH
TLVs Slide21
ReportingMakes a record (by law it has to be kept for 40 years) – procedures need to be in place to ensure such records are maintained. Report has to work for now i.e. be
concise and clear and easily understood. But also be
future proof
– i.e. contain details on QA so it stands up in court in the future.
Must provide appropriate control advice if exposures are high – i.e.
what needs to done to protect the health of workers. Slide22
Any questions? Paul HumphreyChartered Occupational Hygienist
Paul.Humphrey@ghtechnical.com
Mob. 07944 629544
www.ghtechnical.com