Document MXzaDGZgmRGZNvgrYxD5374L
V K 3.U g ^ O & 00669B
bibliographic 0*1 a SHEET
4,, irtJt tititi ''uMjjJr
I. Repon No.
EHS-7W
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Asbestos Fibers in Ambient Air of California
V7*. A ui hr-f *) Jack C. Murchio, W. Clark Cooper and Arturo DeLeon
9< Orff 4 fttzui i on Ha me sod Addre** School of Public Health University of California, Berkeley, CA.
2. Recipient1* Acee,.,,,. Nu.
5. Report D.te Harsh 1, 1973
6.
t. Ptriorming Orpinizit lun Kept.
up. EHS-73-2 10* Hroicct/TfcAk/tt'urit Unf No, AHB-A-054-1
IK Contracl/tsram No.
PCA 274
12. Spaniiwing Otfla.ru jot mn N am* and Add/ea*
Air Resources Board
Resources Agency
13. Type of Report fit Period Covered
Final 7/71-12/72
State of California
1025 P Street, Sacramento, CA. 958l4
15, Supple ternary Notes
The report includes data on ambient asbestos m the San Francisco Bay Area cities
and other locations, from a study funded by the National Insulation Mfr's Assoc. 14. Ai.mriinscontent of freeway air was compared to thalT of ambient air upwind-!rom~
the freeway. Portions of Millipore AA filters containing suspended particulates
collected m Los Angeles at four freeway and four upwind sites were examined for
fiber content with microscopy and transmission electron microscopy (TEM). Electron
micrographs af selected samples are shown. The T3M method is described and compared
with three other TEH methods for asbestos analysis. The technique used in this
study leaves fiber or fibre bundles intact; fibres in unbroken clumps were not
counted. Chrysotile, amphiboles and glass fibers were identified; length and
diameter were measured. Single fibers were counted, including a group of unknowns
which were a substantial part Cfi59>) of the total fibers. Hesults^are tabulated for
120 samples. At freeway sites, chrysotile, amphiboles, glass fibers and unknowns
ranged from 0-100, 0-10, 0-4 and 0-l8 f/1, respectively; upwind sample ranges were
0-9, 0-8 and 0-30 f/1, respectively. Freeway samples differed from upwind samples
m fibril content.
and JSi, respectively. ___________________________________
17. key Words od Document Analynt, 17a. Descriptor!
Chrysotile Amphiboles
Particle size distribution Concentration (composition)
Glass fibers Electron microscopy . Microscopy
Motor vehicles Quantitative analysis Brake linings
Freeways
Disposal
Atmospheric composition __ Air pollution
Talc Sampling
Counting
17b. Identifirr./Opcn-Ended Term.
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TABLE OF CONTENTS
Summary and Recommendations
Introduction
1
Methods I Description of sample collection
II Method of air sampling III Analytical Procedure for counting and
sizing fibers by light microscopy IV Analytical Procedure for electron microscopy
Appendix A V Experimental design
k 12
ll
9 16
Results ` Tables 1-lS
18 21-15
Discussion and Conclusions Analysis of chrysotile asbest js fibers in Los Angeles Freeway and Amb tent Air Controls, San Francisco Bay Area and ither locations Chrysotile asbestos fiber fro u brake linings Size distribution of chryaotiLe asbestos Size distribution of chrysotile asbestos Figure 6 Analysis of amphibole asbestos Analysis of glass fibers Analysis of unknown fibers Methods of estimating asbestos fiber concentration in air by electron microscopy Comparison of masB versus f/1 of chrysotile asbestos fibers in New York and Los Angeles ambient air
16 50 53 53A 5*t 55 58
60
67
Appendix A - Analytical Procedures - Electron Microscopy
69
References
77
Acknowledgements
79'
Electron Micrographs
Plate3 I-XIII
Discussion, of Plates
19,51,59
The statements and conclusions in this report are those of the contractor and not necessarily those of the California Air Resources Board. The mention of commercial products, their source or their uco in connection with material reported herein is not to be construct as either an actual or implied endorsement of such products,
006693
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SUMMARY This report summarises estimates, by electron and light microscopy, of the'nuaber and size distribution of fibe*s collected on membrane filters from air in four Los Angeles freevsy sites, upwind" ambient air controls, and is ambient air from San Francisco Bay Area Cities and other California locations. The chrysotile asbestos fiber concentration in the air at all locations is low in the range of 2ero - 10 fibers/liter. Based upon com parison of fiber concentration in various sites upwind and downwind, and at various distances from freeways, motor vehicles using the Los Angeles freeway system do not appear to be an inriortant source of airborne ehrysotile asbestos fibers. The Los Angeles samples do not differ appreciably in fiber concentrations of chrysotile asbestos from the San Francisco Bay Area samples. The concentration of glass and unidentified fibers was estimated in the Los Angeles and San Francisco Bay Area samples and found to be low i.c. in the same order of magnitude as for chrysotile asbestos. The concentra tion of amphibole asbestos fiberB in the air were estimated in the Los Angeles freeway sites and found to be in the same order of magnitude as the chrysotile asbestos concentration. A method is described far the use of electron microscopy suitable for quantitative analysis end identification of chrysotile and amphibole asbestos fibers in ambient air end at emission sources.
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