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HASKELL LABORATORY MEDICAL RESEARCH PROJECT MR-1311
Pu3tine33 of Thermal Insulating Materials
_ Introduction
The study which is reported herein is part of a study initi ated by the Thermal Insulation Group of the Engineering Services Division.
Purpose
The purpose of the study was to attempt to devise a means of measuring the comparative du3tine3s of several competitive insula ting materials in relation to the risk of injury to health during their installation, use, removal, and disposal.
The health risk in working with thermal insulating materials consists of the danger of contracting lung disease from excessive inhalation of fine dust, including, in particular, asbestos fibers. The magnitude of the danger is dependent upon (a) the amount of dust inhaled, (b) its particle size, and (c) the composition of the crystalline particles or fibers. Glossy, non-crystalline particles and fibers have not been implicated in producing lung disease.
In this study we attempted to compare the amounts of dust generated from each of the test materials when subjected to mechanical energy in a repeatable, reproducible manner, to examine the relative amounts of coarse and fine particles, (roughly the irrespirable and the respirable) and to examine the crystallinity of the fine dust by x-ray diffraction.
Methods
The tests were carried out at the Engineering Test Center by Engineering Department personnel jointly with Haskell Labora tory personnel. They were done in a small, closed room at the Center in which there was a minimum of air movement.
The thermal insulating materials that were chosen for entry into the comparative series were furnished by the Engineering Service Division. They were in the form of slabs-, 2 inches thick. Mechanical energy was applied to the slab by making a series of 18-inch cuts with a circular table saw operating at a fixed speed. The cuts were timed and the times were held constant for all of the materials. The sequence that was followed in making the cuts
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Dustiness of Thermal Insulating Materials (Cont`d)
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and in collecting samples of airborne dust is presented in Appendix A.
Sampling Equipment.
Three series of samples of airborne dust were collected sirautaneously during the sawing and another three series were collected after the dus^ had had time to settle out of the air. The first series consisted of a sample collected by drawing air through a raillipore membrane filter (0.8 micron pore size) by means of a Unico Telmatic Air Sampler; a second series was collected by draw ing air through a similar filter by means of a small battery oper ated personal sampler of the type that has been in use in the con struction division for the past couple of years. The third series of samples was^ collected by means of the Unico 550 Turbinjet High Volume Air Sampler. It pulled the air first through a Model 240 Cyclone Separator. The fine fraction of dust passed through the cyclone and was deposited on Whatman No. 41 filter paper. In Appendix A, the high volume sampler is referred to as Hi-Vol and the millipore filter sampler is referred to as M. F.
Fiber Counts.
Thejnillipore filters from both the Telmatic samplers and the construction division samplers were used for counting fibers according to the method currently in use by the U. S. Public Health Service. This is a count with a 430 x magnification, using phase contrast illumination and counting all fibers greater than 5 microns in length.
Weight Determinations.
The cyclone separators were each weighed before and after dust collection and the difference was recorded as the weight of coarse dust. Each of the Whatman filter papers was weighed before and after collection and the difference was recorded as fine dust.
X-Ray Diffraction.
The filter papers on which had been deposited the fine dust were submitted to the Chemical Physics Department, Carnegie-- Mellon University, for identification of the minerals by means of x-ray diffraction.
Statement of Results
Fiber Counts.
The results of fiber counts are presented in Table 1. In this table the designation C after the Roman numeral identification of each material refers to the sample collected by the use of the
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construction division sampling equipment. The fiber counts that were obtainedjErom the raillipore filter used with the Telmatic sampler during sawing are presented in Figure 1. Figure 2 gives the results obtained from the millipore filter samples collected with the Telmatic sampler after settling. Figures 3 and 4 pre sent graphically the counts obtained from the millipore filter samples collected by use of the construction division sampling equipment during sawing and after settling respectively.
Weight Determinations.
In Table 2 are presented the results of the weighings of the cyclone separators and the filter papers with the calculated ratio of the coarse to the fine fractions. The ratios are plotted graphically in Figure 5 and Figure 6 representing the ratios dur ing sawing and after settling respectively.
It will be noted that air volumes were not equal for all of the samples collected. It was satisfactory to calculate ratios of coarse to fine fractions with the weights that were actually obtained, but in order to make a meaningful comparison of the quantity of the fine dust generated by the sawing per unit volume of air, it became necessary to adjust the weights of the fine fractions to _an equal air volume for all samples. The results are given in Tables 3 and 4 and they are plotted graphically in Figures 7 and 8.
Results of X-Rav Diffraction Analysis.
The fine fractions of dust that were deposited on Whatman 41 filter paper after passage thru the cyclone separator were sub mitted for analysis by means of the Debye-Scherrer technique. The results are presented in Appendix B.
It will be noted that with each material the composition as seen by x-ray diffraction remains the same for the fraction col lected during-sawing and that collected after settling. This rules out any selective settling of components of the mixture on a scale sufficient to influence the health effects of inhaled particles before and after settling.
The finding with respect to Unibestos is clear-cut. It con sists of aroosite asbestos.
In the group represented by Calsilite SS, Super-Caltemp, and Thermasil? and in the group consisting of Kaylo 20, the report states a possibility of the presence of either amosite or crocidolite. This question should be settled by reference to the suppliers because crocidolite would be less desirable from the health standpoint.
There are reports of disease having occurred from relatively brief exposures in contrast to the slowly developing effects from long exposure in the case of the other asbestos forms.
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If crocidolita
is absent, the groups containing Calsilite SS
Super-^altemp, Thermasil, and also Kaylo 10 STS and JM Silicated *
Thermobestos are about equal with respect to composition: they are
all mainly a non-asbestos mineral (tobermorite) and about 10 per
cent of an asbestos. Minerals like tobermorite are classed among
the "inert" qr nuisance particulates with respect to health effects,
e.g., Portland Cement.
Kaylo 20 was found to contain a higher asbestos content, and also an unidentified crystalline material.
Comparison of Materials.
Table 5 presents a conditional ranking of the subject materials based strictly upon the numerical results of fiber counts, weights of fine fractions and the ratios of coarse to fine fractions for each material.
This classification, even when combined with the composition data, gives no clear-cut indication of superiority.
It may be reasoned that Kaylo 10 STS and JM Silicated Therrao-
bestos, both of which have low asbestos content, performed remark ably well with respect to numbers of countable fibers and favorable
weights of fines and ratios of coarse to fine.
The I&B Material and the Unibastos gave comparatively high fiber counts but were lowest in weight of fines and extremely favorable in ratio of coarse to fine fractions. It should be remembered that the fiber counts were made on whole airborne samples collected on mem brane filters without prior size-separation. The I&B Material and
Dnibestos are apparently high in content of fibers that are count
able by optics and by definition, but, when subjected to aerodynamic
size separation, the dust cloud from both materials yielded extreme ly low weight of fines. Unibestos is less desirable on the basis of asbestos content.
Calsilite SS, Super-Caltemp, and Thermasil behaved in a similar range of performance with respect to fiber counts and weights of fine fractions, A strong point in their favor is the low asbestos
content (unless it should be crocidolite).
Kaylo 20 is a favorable material with respect to fiber counts and weights of fines. More information should be sought on its asbestos content before passing judgment.
J. F. Morgan/bjd
Haskell Laboratory December 14, 1970
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' TABLE 1
NO. Z I-C II II-C III III-C IV IV-C V
v-c
VIII VIII-C IX IX-C X
x-c
XI
XI-C
XII
XII-C
XIII
RESULTS OF FIBER COUNTS
Material
10 Fibers
> 5 p. per Filter
Unibestos
17.1
Unibestos
11.8
Unibestos
4.9
Unibestos
6.1
Thermasil
2.4
Thermasil
2.5
Thermasil
2.5
Thermasil
1.0
Kaylo 10 STS
1.1
Kaylo 10 STS Kaylo 10 STS Kaylo 10 STS
1.6 1.0 0.71
Kaylo 20 Kaylo 20
9.5 5.3
Kaylo 20
Kaylo 20
JH Silicated _ Thermobestos
6.9 3.6 1.3
^ JM Silicated Thermobestos
0.41
JM Silicated Thermobestos
1.2
JM Silicated Thermobestos
0.46
Calsilite SS
17.5
Air Volume (ml) 14,400 10,400
--
13,000 21,600 10,400 24,000 14,000 22,400 10,400 28,000 13,000 22,400 10,400
28,000 13,000 22,400
Fibers >5u Der ml
1180 1130
--
470 111 240 104
72 49 154 36 55 424 510 246 277 58
10,400
40
28,000
43
13,000
35
22,400
780
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TABLE 1 (COOT'D)
No. XIII-C XIV XIV-C XVII XVII-C XVIII XVIII-C XIX XIX-C
XX XX-c
XXI XXI-C XXII XXII-G XXIII XXIII-C XXIV XXIV-C XXV
xxv-c
-- RESULTS OP FIBER COUNTS (CONT*D)
Material
10 Fibers
> 5 p. per Filter
Air
Volume ' fml)
Calsilite SS
12.3
10,400
__ Calsilite SS*
7.9
28,000
Calsilite SS*
3.7
13,000
-- Super-Calterap Super-Caltemp
23.1 23.3
22,400 10,400
__ Super-Calterap
30.5
28,000
Super-Ca1temp Unibestos
7.5 **
13,000 22,400
Unibestos 61 10,400
Unibestos unibestos
77.7 10.7
28,000 14,500
Therma3il
34.7
22,400
Thermasil Thennasil
12.3 10.2
10,400 28,000
Thermasil
4.0 13,000
Calsilite SS Calsilit*e SS
42.0 4.4
22,400 12,000
Calsilite SS Calsilite SS
11.4 3.7
28,000 14,500
I&B Material 1185-31,32,33
44.1
22,400
I&B Material 1185-31,32,33
24.4
10,400
Pibers
>ne5r Pm,l
1180 282 284
1030 2330 1088
577 **
5870 2780
740 1550 1180
366 307 1870 367 408 255 1960
2440
* There was a 4-minute delay in start. ** Reported too dense to count.
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iSSIJ
i TABLE 1 (COOT'D)
No. XXVI
XXVI-C
; results op fiber counts (cont'd)
Material
106 Fibers
> 5 ju per Filter
Air volume (ml)
I&B Material 1185-31,32,33
10.9
28,000
I&B Material 1 1185-31,32,33
6.8
13,000
Fibers >5u per ml
390
523
oHr
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TABLE 2
-SIZE SEPARATED SAMPLES (Unico Cyclone - Whatman 41 Paper)
Unibestos Therraasil Kaylo 10 STS Kaylo 20
Purine Sawing _____________________ After Settling
Wt.Coarse Wt.Fines Ratio
Wt.Coarse Wt.Fines Ratio
gm gm Coarse/Fine gm gm Coarse/Fine
^Xo.osgo 0.0484
1.8388
XX0.0426 0.0186
2.2903
XXI .0432
.0773
.5589
XXII.0196
.0309
.6343
V .0548 0.0993
0.5519 V1II0.0438 0.0274
1.5985
IX.0211
.0388
.5438
x.0056
.0003 ^ 18.66{`
JM Silicated Therraobestos
Calsilite SS
XI .0922
XIII.0444
XXIII.0490
Super-Calterap
XVII.0449
I&B Material
XXV.0872
.0701 .1235 .0930 .1103 .0142
1.315 .3595 .5269 .4021
6.1408
XII .0468
^.0135 ""*0151
xxvx.0!61
.0367
1.275
.0282 0.4787
.0476
0.3172
.0459
.2919
.0024 6.7083
^Apparently anomalous.
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TABLE 3
DUST WEIGHTS. SIZE SEPARATED SAMPLES
(Unico Cyclone - Whatman 41 Paper)
Adjustment of weights of fine fractions for equal air volumes.
A. During Sawing Average air volume for all samples: 70.9 ftJ
Material
Semple No.
Kaylo 10 STS* V
Kaylo 20
IX
JM Silicated Thermobestos
XI
Calsilite SSL
XIII
Super-Caltemp
XVII
Unibestos
XIX
Thermasil
XXI
Calsilite SS
XXIII
I&B Material
XXV
Air Vol. (ft3) 71.36 78.72
69.28 61.60 67.28 79.20 67.28 64.16 79.20
Wt. Pines (am)
0.0993 .0388 .
.0701 .1235 .1103 .0484 .0773 .0930 .0142
Equivalent wt. Fines
0.0986 0.0350
.0716 .1420 .1160 .0433 .0814 .1025 .0127
09**60
t-wasmi t~ i i--i.iwt.i-a..3ii^.jeiii
lisamMB&aiMiaissu
TABLE 4
. DUST WEIGHTS. SIZE SEPARATED SAMPLES = (Unico Cyclone - Whatman 41 Paper)
Adjustment of weights of fine fractions for equal air volumes. B. After Settling
Average air volume for all samples: 98 ft^
Material
Sample NO.
Kaylo 10 STS ^ VIII
Kaylo 20
*X
Air,Vol. (ft3) 98.5 '
99
JM Silicated Thermobestop
XII
Calsilite SS
XXV
Super-Caltemp XVIII
96.5 99 99
Unibestos Therraasil
XX XXII
99 95.4
Calsilite SS XXIV.
I&B Material XXVI 1185-31,32,33
96.5 99
Wt. Pines (am)
0.0274
0.0003*
Equivalent Wt.Pines(am)
0.02725
.0367 .0282 .0459 .0186 .0309 .0476 .0024
.0372 .0279 .0454 .0184 .0137 .0483 .0024
* Apparently anomalous. Not to be plotted.
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TABLE 5
. CONDITIONAL RANKING OF MATERIALS
Fiber Cfounts Telroatic Sampler
During After Sawing Settling
Fiber <founts
Constnaction Sam]aler
During Sawing
After Settling
Weights Fine Fract ions
During After Sawing Settling
Ratios oi- Weights Coarse t:o Fine
During After Sawing Settling
Kaylo Kaylo 10 STS 10 STS
JM Sil. Thermo.
JM
Sil.
I&B .
I&B
I&B
I&B
Thermo. Material Material Material Material
JM
Sil. Thermo.
JM
Sil. Thermo.
Kaylo 10 STS
Kaylo 10 STS
Kaylo 20
Unibestos
Unibestos
Unibestos
BEST
__________________________________________________
Kaylo 20
Kaylo 20
Calsilite Calsilite UniSS SS testos
JM Sil.
Thermo.
Calsilite Calsilite Kaylo SS SS 20.
Kaylo 20
JM
Sil. Thermo.
Kaylo 10 STS
Therma- Kaylo sil 10 STS
Super- ThermaCaltemp sil
Tharma- Therraasil sil
Thermasil
Thermasil
Kalo 10 STS
JM
Sil. Thermo.
Thermasil
I&B Material
SuperCalterap
I&B Kaylo Material 10 STS
JM
Sil. Thermo.
Kaylo 20
Thermasil
I&B SuperMaterial Caltemp
I&B SuperMaterial Caltemp
SuperCaltemp
Super-
Caltemp Calsilite Calsilite SS SS
Unibestos
Uni tes tos
Uni tes tos
Unibestos
Calcilite Caleilit Super r SS SS Calterap
Super" Caltemp
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