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The value of microscopy analysis Garry Burdett Health and Safety Laboratory Harpur Hill, Buxton, UK, SK17 9JN

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The value of microscopy analysis Garry Burdett Health and Safety Laboratory Harpur Hill, Buxton, UK, SK17 9JN. Asbestos Hazard. Mortality (excess deaths) due to: Fibrosis of the lung (asbestosis) Cancer of the lung (bronchial cancer etc) Cancer of the lung lining (e.g. mesothelioma) - PowerPoint PPT Presentation

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Page 1: Asbestos Hazard

The value of microscopy analysis

Garry BurdettHealth and Safety Laboratory

Harpur Hill, Buxton, UK, SK17 9JN

Page 2: Asbestos Hazard

Asbestos Hazard

• Mortality (excess deaths) due to:– Fibrosis of the lung (asbestosis)– Cancer of the lung (bronchial cancer etc)– Cancer of the lung lining (e.g. mesothelioma)

• Morbidity (lung changes/dysfunction)– Pleural plaques;– Diffuse pleural effusions

Page 3: Asbestos Hazard

Fibre Related Risk:

• Depends on:– Dimensions– Durability / Type– Dose / Exposure– Time

(Measurable by microscopy)

Page 4: Asbestos Hazard

EU Directive: Dimensions

• For the purposes of measuring in the air, only fibres with a length of more than five micrometres, a breadth of less than three micrometres and a length to breadth ratio greater than 3:1 shall be taken into consideration.

(2003/18/EC amending to EU asbestos worker protection directive (83/477/EEC) article 7.6 )

Page 5: Asbestos Hazard

Durability / Type

500

100

10

100

200

300

400

500

Ris

k fa

ctor

Crocidolite Amosite Chrysotile

Asbestos type

Fig 1: Mesothelioma risk by fibre type

Page 6: Asbestos Hazard

Dose / Exposure

• Exposure is used as a surrogate for dose by sampling a known volume of air onto a membrane filter and counting the numbers of fibres present in a known area.

• This is used to calculate the fibre concentration in f/ml or f/cm3 of air.

• Uses size criteria to determine ability to reach pulmonary region of the lung.

Page 7: Asbestos Hazard

Time

• Dose = exposure x duration (f/ml/years)• Risk cumulative dose (assume linear);• Risk time since first exposure

(mesothelioma related by power law).• Lag time 15 – 60 years from exposure to

disease symptoms

Page 8: Asbestos Hazard

EU directive: Fibre Counting

• “Fibre counting shall be carried out whenever possible by PCM (Phase contrast microscope) in accordance with the 1997 (World Health Organisation) recommended method (16) or any other method giving equivalent results.”

Page 9: Asbestos Hazard

EU Directive: Requirements

• The 2003 amendment to 83/477/EEC abandoned action levels and different control levels for different types of asbestos and introduced a single limit of 0.1 f/ml over an 8-hour time weighted average. (Article 8)

• Therefore the EU regulation for controlling the risk to workers, require only PCM fibre number information over a broadly defined size range.

• Article 4 requires the type and quantities of asbestos handled to be notified

Page 10: Asbestos Hazard

Main types of microscopy for fibre counting.

• Phase contrast light microscopy PCM • Scanning electron microscopy SEM• Transmission electron microscopy TEM.• All have ISO or WHO standard methods

• Polarised light microscopy PLM for bulk analysis.

Page 11: Asbestos Hazard
Page 12: Asbestos Hazard

PCM (X500 magnification)

Page 13: Asbestos Hazard

SEM

Page 14: Asbestos Hazard

TEM

Page 15: Asbestos Hazard

SEM higher Mag & 3D

Page 16: Asbestos Hazard

TEM high mag chrystotile

Page 17: Asbestos Hazard

PLM : Dispersion staining

Page 18: Asbestos Hazard

Discrimination of fibre type

• PCM: No discrimination or identification ;• PLM Uses optical properties + refractive

index/ dispersion colours to identify fibres; >0.8µm width;

• SEM uses Energy Dispersive X-ray analysis to semi-quantitatively measure chemistry;

• TEM uses quantitative EDX and electron diffraction to identify fibres.

Page 19: Asbestos Hazard
Page 20: Asbestos Hazard

Comparison of methods for fibre counting

Operating Mag

Area (mm2) examined

Time taken(mins.)

Rate area examinedmm2/hr

PCM X500 (200 fov) 1.5

20 4.5

SEM X2000 (50 fov)0.15

30 0.3

TEM x5000 (50 go)0.5

40 0.75

Page 21: Asbestos Hazard

Likely upper limit of detection (f/ml) by method and volume

WORK ENVIRONMENTAL

COST PER HOUR

VOLUME(litres)

500 3000

PCM 0.01* 0.0017* 30-50

SEM 0.015 0.0025 80 - 120

TEM 0.005 0.0007 80 - 120

Page 22: Asbestos Hazard

Accuracy & Precision

• Accuracy not usually known.

• Precision includes:– Random “Poisson” counting error– Instrumental errors (QA / calibration)– Human errors (QA / Proficiency testing)

Page 23: Asbestos Hazard

Random counting errors (95%)

No. of fibres

Lower limit

Upper limit

No. of fibres

Lower limit

Upper limit

0 0 2.99 5 1.624 11.669

1 0.025 5.572 6 2.202 13.060

2 0.242 7.225 10 4.795 18.39

3 0.619 8.767 20 12.217 30.889

4 1.090 10.242 50 37.112 65.919

Page 24: Asbestos Hazard

Quality and accreditation

• Quality assurance and proficiency testing is essential, particularly if results from different analysts and laboratories are being used or compared.

• Accreditation of Laboratories to ISO 17025 mandated by the EU directive.

Page 25: Asbestos Hazard

Type of analysis

PCM SEM TEM PLM

Fibre counting of air samples 

Belgium (25)France (?)Netherlands(20)Spain (20)UK (200) 

Germany*  

France (20) Not applicable

Fibre Identification of bulk samples

Not applicable UK (5) UK (17) UK (250)

Fibre counting and identification of air samples

Not applicable Germany* 

France (20) Not applicable

* PT scheme run for one or two rounds in past a new scheme was plannedNote: UK schemes also include a number of EU countries who participate

Page 26: Asbestos Hazard

RICE: Fibre counting PT

• RICE - 187 labs.• MMMF – 12 labs.• ERM – WHO major change

Chart 1. RICE Ratings

196 197 195 192 190 193 194 186 189 190 184 184 183 184 184

0

50

100

150

200

250

52 53 54 55 56 57 58 59 60 61 62 63 64 65 66

Round

Num

bers

of l

abor

ator

ies

Rating 1

Rating 2

Rating 3

Page 27: Asbestos Hazard

AIMS: Fibre Identification PT

Chart 4 : Distribution of cumulative scores for rounds 22 - 24 (UK Laboratories)

25%

33%

19%

22%

1%

0 (No Errors)

7 (1 Minor Error)

8 - 20

21 - 47

> 47

Page 28: Asbestos Hazard

Value of PCM counting

1. Workplace exposure can be controlled using the WHO - PCM method;

2. Counts “regulated” WHO fibres & meets EU criteria;

3. Relatively quick (on-site) and cheap;4. Environmental exposure can be

screened by PCM.

Page 29: Asbestos Hazard

PCM Limitations

1. PCM has limited detection due to background counts on blank filters (0.01 f/ml);

2. No knowledge of fibre types;3. Only an “index of exposure”

Page 30: Asbestos Hazard

Value of analytical SEM

• Can be adjusted to give regulated fibre counts,

• Can give fibre size information,• Classifies fibre types present using EDX

spectra data.

Page 31: Asbestos Hazard

SEM limitations

• Limited availability;• Off site analysis;• Costly • Can only be used for regulated fibre

counting,• No definitive identification of fibres,• Lowest area of filter scanned per field of

view.

Page 32: Asbestos Hazard

Value of TEM

• Can count regulated fibres + all fibre sizes.• Accurate size information,• EDX chemical analysis of all fibre sizes • Crystal structure information (SAED)• Identification of fibre type,• Can give complete information on all fibre

sizes if needed

Page 33: Asbestos Hazard

Limitations of TEM

• Limited availability;• Off site;• Costly

Page 34: Asbestos Hazard

Recommendations 1

• Use PCM for workplace control and checking after clean –up (with disturbance sampling).

• Indoor and near source environmental use PCM screening and SEM or TEM analysis (as necessary) on selected half-filters.

• Ambient air: Analytical TEM is best, SEM is more limited, PCM not very useful.

Page 35: Asbestos Hazard

Recommendations 2

• Use Polarised light microscopy (PLM) for analysis of bulk samples for asbestos present and type of asbestos.

• Use PLM to screen minerals and soils for asbestos content.

• Asbestos in water usually analysed by TEM