Philip Morris
Identification of Asbestos by Polarized Light Microscopy
Fields
- Author
- Delly, J.G.
- Mccrone, W.C.
- Type
- SCRT, REPORT, SCIENTIFIC
- ABST, ABSTRACT
- BIBL, BIBLIOGRAPHY
- CHAR, CHART, GRAPH, TABLE, MAPS
- DRAW, DRAWING
- FOOT, FOOTNOTES
- Area
- SOLANA,RICHARD/CENTRAL FILES
- Litigation
- Fali/Produced
- Characteristic
- EXTR, EXTRA
- MARG, MARGINALIA
- MISS, MISSING PAGES
- Site
- R545
- Named Organization
- Natl Bureau of Mines
- Author (Organization)
- Mccrone Associates
- Workshop on Asbestos
- Named Person
- Deer
- Delly, J.G.
- Draftz, R.
- Howie
- Leineweber, J.
- Wolkodoff, V.
- Zussman, J.
- Master ID
- 2063104795/5283
- 2063104795-5283 Proceedings of Workshop on Asbestos: Definitions and Measurement Methods Proceedings of A Workshop on Asbestos Held at the National Bureau of Standards, Gaithersburg, Maryland, 770718 - 770720
- 2063104803-4820 History of Asbestos - Related Mineralogical Terminology
- 2063104821-4835 Fibrous and Asbestiform Minerals
- 2063104836-4849 the Crystal Structures of Amphibole and Serpentine Minerals
- 2063104850-4864 the 'asbestos' Minerals: Definitions, Description, Modes of Formation, Physical and Chemical Properties, and Health Risk to the Mining Community
- 2063104865-4870 General Discussion of Mineralogical Aspects
- 2063104871-4893 Epidemiological Evidence on Asbestos
- 2063104894-4918 Measurement of Asbestos Retention in the Human Respiratory System Related to Health Effects
- 2063104919-4930 Epidemiologic Evidence of the Effect of Type of Asbestos and Fiber Dimensions on the Production of Disease in Man
- 2063104931-4940 Pathophysiology in Relation to the Chemical and Physical Properties of Fibers
- 2063104941-4949 the Carcinogenicity of Fibrous Minerals
- 2063104950-4958 Niehs Oral Asbestos Studies
- 2063104959-4973 Epa Study of Biological Effects of Asbestos - Like Mineral Fibers
- 2063104974-4985 A Study of Airborne Asbestos Fibers in Connecticut
- 2063104986-4995 General Discussion of Relationship Between Chemical and Physical Properties and Health Effects
- 2063104996-5015 Identification of Selected Silicate Minerals and Their Asbestiform Varieties
- 2063105016-5029 An Overview of Electron Microscopy Methods
- 2063105044-5064 Mineral Fiber Identification Using the Analytical Transmission Electron Microscope
- 2063105065-5074 Transmission Electron Microscopical Methods for the Determination of Asbestos
- 2063105075-5088 Statistics and the Significance of Asbestos Fiber Analyses
- 2063105089-5106 Selection and Characterization of Fibrous and Nonfibrous Amphiboles for Analytical Methods Development
- 2063105107-5117 Asbestiform Minerals in Industrial Talcs: Commercial Definitions Versus Industrial Hygiene Reality
- 2063105118-5131 the Detection and Identification of Asbestos and Asbestiform Minerals in Talc
- 2063105132-5146 Misidentification of Asbestos in Talc
- 2063105147-5155 Ambient Air Monitoring for Chrysotile in the United States
- 2063105156-5167 Environmental Protection Agency Interim Method for Determining Asbestos in Water
- 2063105168-5171 Inter-Laboratory Measurements of Amphibole and Chrysotile Fiber Concentration in Water
- 2063105172-5177 the Standard for Occupational Exposure to Asbestos Being Considered by Astm Committee E-34
- 2063105178-5193 Identification and Counting of Mineral Fragments
- 2063105194-5202 Practical Aspects of Talc and Asbestos
- 2063105203-5210 General Discussion of Analytical Methods
- 2063105211 Introduction
- 2063105212-5219 the Mining Enforcement and Safety Administration - Regulations and Methods
- 2063105220-5229 Occupational Safety and Health Administration Methods
- 2063105230-5236 FDA Projects and Methods
- 2063105237-5238 Cosmetic Talc Powder
- 2063105239-5248 Cpsc Regulation of Non-Occupational Exposure to Asbestos in Consumer Products
- 2063105249-5255 Impact of Asbestos Regulations on the Mining Industry
- 2063105256-5265 General Discussion of Regulatory Aspects
Related Documents:
Document Images
V
National Bureau of Standards Special Publication 506. Proceedings of the Workshop on
Asbestos:- Definitions and Measurement Methods held at NBS, Gaithersburg, MD, July 18-20,
1977. (Issued November 1978)
IDENTIFICATION OF ASBESTOS BY POLARIZED LIGHT MICROSCOPY
Walter C. McCrone
(Paper presented by John G. Delly)
McCrone Associates, Inc.
Chicago, Illinois 60616
Abstract
A number of analytical tools can be used to characterize and
identify asbestos: infrared absorption, x-ray diffraction, DTA, SEM,
TEN, and the light microscope. Each has advantages and limitations. The
polarized light microscope (PLN) has many advantages, and the only
disadvantages are 1) the asbestos particles must be at least a micrometer
in largest dimension, and 2) considerable training in optical
crystallography is needed.
PLM, on the other hand, is very sensitive (ppm range), extremely
rapid (1-5 minutes to identify all components of most samples) and, of
all the methods, only PLM will identify the individual amphiboles.
Key Words: Amphiboles; asbestos; dispersion staining; microscopy.
There are a number of analytical methods useful for the identification of asbestos.
These include infrared absorption (IR), x-ray diffraction (XRD), differential thermal
analysis (DTA), scanning electron microscopy (SEM), transmission electron microscopy
(TEM) with or without electron microprobe analyzer (EMA), and polarized light microscopy
(PLM) with or without dispersion staining (OS). Each has advantages and disadvantages.
Every analyst uses and should use the techniques in which he has the required
training and with which he feels confident. At the same time, every sample should
ideally be analyzed by the most suitable technique. Occasionally, of course, it may be
wise to use two or more techniques and this is certainly true for asbestos. We would like
to summarize our attitude toward the various techniques for asbestos and describe in more
detail the technique we feel has many advantages and is under-utilized; this is polarized
light microscopy, especially when supplemented by dispersion staining. First, however,
the advantages and disadvantages of each technique:
TEM is most useful for the detection and identification of asbestos fibers smaller than
the resolving power limit of the PLM. This is usually the case for water or beverages in
general. Quantitative procedures are available so that the number, size, and identity of
asbestos fibers per unit volume can be accurately determined. Identification by TEM depends
on selected area electron diffraction (SAED). Occasionally energy or wavelength dispersive
detectors are fitted to the TEM to make possible elemental analysis of individual fibers.
Nothing can compete with TEM for the analysis of samples containing subpicogram particles.
SEM has no advantage over TEM except that it takes prettier pictures. It will also
fail To- see the smallest fibers, and lacking SAED it cannot identify all fibers. The
energy dispersive detector on most SEMs is not as effective as the wavelength dispersive
detectors on some TEMs and SEMs.
XRD is a useful method since it can be made quantitative. However, it cannot tell
size or shape, is not very sensitive (about 1 percent or a bit better), and does not
differentiate between most of the amphiboles. At best it supplements other techniques.
235
2063105030

IR and DTA can also be dismissed for all except routine samples containing high
percentages oi-asbestos.
This brings us to PLM and 5 on which we wish to spend more time because of our
conviction that, of all the eicroanalytical techniques for asbestos, it is by far the most
effective. It is the only method depending on the unique optical crystallographic
properties of the various crystal phases in the sample. These properties - refractive
indices, dispersion of refractive indices, birefringence, sign of elongation and extinc-
tion angle - are unique to the crystalline state and therefore unequivocally identify
chrysotile, anthophyllite, tremolite, actinolite, grunerite, cummingtonite, etc.
The background for dispersion staining has been adequately covered elsewhere [13i.
Very briefly, it imparts color to any transparent particle mounted in a liquid whose
dispersion curve intersects the dispersion curve for the particle in the visible. The
colors, related to this matching wavelength, characterize and identify any given sub-
stance. With polarized light, isotropic substances show a single characteristic color, but
anisotropic substances show different colors corresponding to the different refractive
indices in different orientations. Chrysotile, for example, shows blue and blue-magenta
colors, crosswise and lengthwise respectively, for each needle crystal when mounted in
Cargille high dispersion liquid nps = 1.550.
The colors shown by the various types of asbestos and a few other associated minerals
are indicated in Figures 1-20 by the wavelengths on each crystal view. These are the
wavelengths at which the liquid indicated and that direction in the crystal have the same
refractive index. This matching wavelength, ao, determines the dispersion staining colors.
TALC
Mg8(S18020)(OI)4
In 1.55 (H.D.): n's (D, H, Z) *
360
497
y m 1.589-1.600
5990.05(-)
This sample (Vermont):
a II 1.546
0= 1.588
y= 1.589
8 = 0.045 (-)
* Deer, Bovie and Zussman.
Figure 1. Dispersion staining colors shown by talc crystals in Cargille high dispersion
liquids nD = 1.550 and n0 = 1.580.
'Figures in brackets indicate the literature references at the end of this paper.
p 9K 360
_, MQo_, «A
a=645 nID 0 - 1.589-1.594
N
O
w
236 ~.
0
~
0
w
~

CHLORITE
(Mg, Al, Fe)12((Si' AI) 8020) (0R)16
In 1.55 (H.D.):
pale yellow to golden yellow
In 1.580 (H.D.):
529 nm
= 420 nm
513nm
a= 529 nm
~+~-- 420 nm
p = 513 nm
Figure 3. Chrysotile.
IL
n's (D, H, Z)
aa 1.57-1.66
S ~ 1.57-1.67
y ~ 1.57-1.67
5 = 0-0.01
Figure 2. Chlorite.
The sample (Caiifornia):
a=1.586
$=1.587
y = 1.598
5 = 0.010 (+)
CHRYSOTILE
Mg3[S12O51(O1i)4
In 1.550 (H.D.);
a= 660 nm
FEj ~ 530 ma , '(y
p- 558nm
n'e(D,$,Z)
a- 1.5324.549
S = 1.540-1.553
y s 1. 545-1.558
5 = 0. 013-0. 007 (-)
Kingte Mine, Quebec Sample -a= 1.5444
9-1.5525
y= 1. 5555
5 = 0. 0111
ANTIGORITE
Mg3(Si205)(OH)4
In 1.550 (H.D.);
F3; Y$1W--r
=3na...,.~~~
Figure 4. Antigorite.
n's (D, H, Z)
a~ 1.558-1.587
~ ~ 1. 56 -1.57
y s 1. 562-1.574
5 = 0.004-0. 007 ( )
This sample:
a=1.555
A= 1.559
y= 1.561 N
~
5 = 0.008 (-) W
237 O
S
W
N

LIZARDTTE
Mg3(53205) (OH)4
In 1.55 (H.D.); n's (D, H, Z)
520
494 nm
~= 690 nm
~494 nm
undulose extinction
Figure 5. Lizardite.
TREMOLTTE
Ca2(Mg, Fe ~5(Sl 8022)(OH, F)2
(low Fe)
y = 427 nm
530 nm
91460 nm
Figure 6. Tremolite.
a= 1.538-1.544
Q°
y = 1. 546-1.560
6 = 0. 016-0. 008
This sample:
a= 1.545
9911.555
y-1.557
6=0.012 (-)
n'a (D, H, Z)
a = 1.604-1.619
y = 1.627-1.642
8 = 0. 021-0.023 (-)
This sample:
a= 1.599
y= 1.621
8=0.022()
238

ACTINOLITE
Ca2(MB, Fe)5(Si8022)(OH' F)2
(20-80% Fe & 80-20% Mg)
In 1.605 (H.D.):
In 1.640 (H.D.):
n's (D, H, Z)
o= 436 nm a= 1.619-1.668
9=
y = 1. 642-1.687
5 - 0. 023-0. 019 (-)
This Sample (Virginia):
a- 1.633
9= 1.841
y=1.847
5 = 0.014 (-)
Figure 7. Actinolite.
ANTHOPHYLLTTE
(Mg, Fe2+)7(S18022)(OH, F)2
ffi 1.580 (H.D.): n'a (D, H. Z)
In 1.605 (H.D.):
y=395am
p = 370 am
y ~ 300 nm
a= 421 nm
a- 598 nm
Figure 8. Anthophyllite.
a= 1.596-1.694
S = 1.605-1. 710
y= 1.615-1.722
5 = 0.013-0.028
(+) (-)
This sample (Pine Mt., Ga. )
o:= 1.601
p = 1.618
y=1. 628
5=0.027 (-)
239

ANTHOPHYLLITE
(Mg. Fe2+)7(Si8 22)(OH"~2
(Mg> Fe)
In 1.640 (H.D.):
In 1.67:
,, , p = 633 nm
557 am
n's (D, H, Z)
~= 1.596-1.694
~ = 1. 605-1.710
y = 1.615-1.722
6 = 0.013-0.028
(+) (-)
This sample (Connecticut):
n= 1.659
p = 1.666
y=1.674
5a0.015(+)
Figure 9. Anthophyllite.
GRUNERITE
(Fe}2, Mg)7(Bi8022) (OH)2
(high Fe)
ffi 1.670:
In 1.700:
a
= 627 nm
Figure 10. Grunerite.
n'e (D. H, Z)
a= 1.663-1.686
S 21 1.681-1.707
y= 1. 697-1.729
5 = 0.034-0.043 (-)
Thie sample:
a=1.669
5=1.684
y=1.697
b = 0. 026 (-)
240

CROCIDOLITE
Na2Fe32Fe23(Si8022)(OH)2
(no Mg, contains Fe+2)
In 1.670:
0 =386nm
0=418
= 380 nm
nm
In 1. 700:
w= 408 nm E= 1. 624-1.666
a=1.688
0= 1.703
y=1.708
6 = 0.010 (-)
Figure 11. Crocidolite.
APATTTE
Ca5(P04)3(OH, Cl, F)
ln 1.606 (H.D.):
w = 408
= 448 nm
Tn 1.64
E=715nm
Onm
n's (D, H, Z)
Figure 12. Apatite.
n's (D, H, Z)
tt= 1.654-1.701
P - 1.662-1.711
y - 1.668-1.717
6 = 0.006-0.016 (-)
This sample (Orange River,
South Africa):
w - 1.628-1.667
w= 408 nm 6= 0. 001-0. 007 (-)
This sample:
E = 1. 6285
w = 1.6357
6 = 0.0062 (-)
241

FORSTERITE
Mg2SLO4
ln 1. 640 (H.D. ):
n's (D, H, Z)
r **
a= 1.635 -1. 827
~ = 1.651 -1.869
y=1.670 -1.879
6 = 0. 035 -0.052 (+) (-)
*pure forsterite
**plns Fe2t replacing Mg
giving fayalite, Fe2Si04
This sample:
a= 1.643
0 = 1.663
y= 1.682
6 = 0.039 (-)
Figure 13. Forsterite.
HORNBLENDE
)(OH,F7
(Na, K)0.1-0.7Os2(Mg, F 2{, F 3+, Al) 5 (Si 6_7, At 2-1O22 2
ffi 1.605 (H.D): , _ _ ,,,, -,,, n's (D, H, Z)
a= 570 nm
Is. 1.640 (H.D): , _
518nm
475
Figure 14. Hornblende.
a= 1.615-L 705
~ a 1.618-1.714
y a 1.632-1.730
6 - 0.014-0.026 (+)
This sample:
a= 1.843
~ = 1.650
y= 1.660
6=0.017 (+)
242

es
In 1.580 (H.D.):
In 1.605:
WOLLASTONITE
Ca(8103)
n's (D, H, 4
a a= 412 am
a= 1.616-1.640
= 1
628-1
650
p~340nm S
.
.
y = 1.631-1.653
y s< 300 nm
6 = 0. 015-0.013
(-)
This sample:
a= 532 am
Figure 15. Wollastonite.
CALCITE
CaCO3
a= 1. 612
9=1. 628
y=1. 632
6 = 0. 020 (-)
In 1.64 (H.D.): n's (D, H, Z)
s - 1.486-1.550
m - 1.658-1.74
6 - 0.172-0.190 (-)
Tbie sample:
s'= 1.525
c=1.486
~=1.653
6=0.167(-)
Figure 16. Calcite.
243

DOLOMITE
(Ca, Mg)CO3
In 1.64 (H.D.): n'e (D, H, Z)
In 1.67:
Figure 17. Dolomite.
MAGNESTTE
MgCO3
In 1.670:
* **
e = 1.500*-1.520
~ = 1.679 -1.703**
6 = 0.179 -0.185 (-)
*pure dolomite
**plus Fe2+ for Mg
This eamplea
w - 1.677
a's (D, H, Z)
*
e s 1.509-1.563*
w = 1. 700-1. 782
6 = 0.190-0. 218 (-)
*wlth Fe replacing Mg
This sample:
In 1.700:
w=1.694
