Document DDg3X8r24vwVDBq7DdDLjXNJM
Summary report: Semi-annual asbestos survey at
Asbestos-Cemenf Pipe Division
J-M Manufacturing Company, inc. Denison, Texas
Galson Project # S6-350-00
Submitted to: Dr. E. E. Wang Corporate Environmental Control Manager 1051 Sperry Road Stockton, CA 95206
March 31, 1986
Gabon
Technical Services, Inc.
Environmental Sciences Division, 6601 Kirkville Road, East Syracuse, New York 13057
APR. 23 1986
D 001795
Summary report: Semi-annual asbestos survey at Asbestos-Cement Pipe Division J-M Manufacturing Company, Inc. Denison, Texas Galson Project # S6-350-00
Submitted by : (2J Chuck C. Siu, CIH
D 001796
ABSTRACT " This report summarizes the results of the Spring, 1986 half-annual survey for workers' exposures to asbestos at the Asbestos-Cement Pipe Division of J-M Manufacturing, Inc. at Denison, Texas. The results may be summarized as follows:
1. Exposure of 14 out of 31 workers monitored were measured at or above the current Occupational Safety and Health Administration (OSHA) Action Level of 0.07 fiber/cc for daily exposure of 12 hours. The Action Level is the concentration above which routine monitoring and medical examinations are required.
2. Exposure of 7 out of the 31 workers monitored were measured above or close to 0.13 fiber/cc, the lower of the two proposed OSHA 12-hour daily permissible exposure levels (PEL).
3. The slash (wet) saw operator's exposure exceeded 0.33 fiber/cc, the higher of the two proposed daily permissible exposure levels (adjusted for 12-hour shift). His exposure also exceeded 50% of 1.3 fiber/cc, the current OSHA PEL (adjusted for 12-hour shift).
4. The UCL workers were not monitored since operations were suspended on the survey day.
001191 D
Project Personnel J-M Manufacturing, Inc.
Dr. E. E. Wang Mr. Tim Armstrong Mr. Carl Weger
Corporate Environmental Control Manager Denison, TX site coordinator Denison, TX site coordinator
Galson Technical Services, Inc.
Mr. Chuck C. Siu, CIH Mr. Daryl Jahn Mr. Scott Silvey
Project Manager & Laboratory Director
Industrial Hygiene Technician & Laboratory Technician
Computer Programmer
ii D 001798
TABLE OF CONTENTS Abstract Project Personnel
page i
ii
Introduction Sampling and analytical method Permissible Exposure Standards Results
Observations and Recommendations
Appendix I - Sampling and analytical method Appendix II - Field Data Sheets Appendix III - Laboratory Data Sheets
1 1 2 2 6
0 oOAf"
INTRODUCTION
This report summarizes the results of a sampling survey conducted on March 31, 1986 at the Asbestos-Cement Pipe Division of J-M Manufacturing^ Inc. at Denison, Texas. The purpose of the half-annual survey was to monitor worker exposures to asbestos fibers as required by the current Occupational Safety and Health Administration (OSHA) regulations.
The survey was performed by Chuck C. Siu, Certified Industrial Hygienist of Galson Technical Services, Inc., Oakland, California, at the request of Dr. E. E. Wang, Corporate Environmental Manager. Site coordination was provided by Mr. Tim Armstrong and Mr. Carl Weger of the Denison plant.
SAMPLING AND ANALYTICAL METHOD
Sampling and analysis were in accordance with National Institute for Occupational Safety and Health (NIOSH) method #P&CAM 239. This method is required by the current OSHA asbestos regulations for occupational monitoring of asbestos. A more detailed discussion of the method is presented in Appendix I.
1
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GALSON TECHNICAL SERVICES, INC.
PERMISSIBLE "EXPOSURE STANDARDS
Occupational asbestos exposures are governed by the OSHA
permissible exposure levels. The current and proposed
OSHA standards are summarised as follows, along with
those recommended by NIOSH and 1985-86 American
Conference of Governmental Industrial Hygienists
(ACGIH).
Source of Standard
(adjusted) 8-hour .12-hour Ceiling (fiber/cc)(fiber/cc) (fiber/cc)
Current OSHA standard permissible exposure "Action Level" *
1st Proposed OSHA standard 2nd Proposed OSHA standard
2.0 0.1
0.5 0.2
1.3 0.07
0.33 0.13
10.0 --
--
NIOSH recommended standard
0.1
0.07
--
ACGIH recommended standards chrysotile asbestos
crocidolite asbestos
2.0 0.2
1.3 0.13
--
* The Federal OSHA asbestos regulations do not have an "Action Level" explicitly stated. 0.1 fiber/cc has been interpreted as an index above which routine monitoring and medical examinations should be implemented.
RESULTS
Before entering into the discussion of the results, the following items should be kept in mind:
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GALSON TECHNICAL SERVICES, INC.
1. Several work positions were not in operation on the survey day, consequently those workers were not monitored. They are listed as follows:
UCL operator, Coupling Cut-off, Boring Mill, Power Sweeper, Coupling Tester and Lining Service.
2. The work positions to be sampled were selected by the plant manager prior to the survey: selection was based on sampling results from previous surveys.
3. Since the work activity levels for these work positions were considered fairly steady throughout the shift, samples of 4-hour durations were collected and their results assumed representative of the whole day exposures
4. Most personnel monitored work a 12-hour shift, the remainder an 8-hour shift and are listed below:
electricians, mechanic, moulding department and utility truck driver.
Results are summarized below and in Table 1, and pertinent field and laboratory data sheets are included
3 Q 00A802
GALSON TECHNICAL SERVICES, INC.
in Appendices II and III. The general locations of most of the work positions monitored are shown on Figure 1.
1. Of the 5 persons who worked an 8-hour shift, their exposures ranged from less than 0.03 to 0.04 fiber/cc. These values were below the 8-hour Action Level of 0.1 fiber/cc. (Action Level is the concentration at which routine monitoring and medical examinations are required to be given to the workers.)
2. Among the 26 workers who worked a 12-hour shift, 12 measurements were below and 14 were above the current Occupational Safety and Health Administration (OSHA) Action Level of 0.07 fiber/cc adjusted for 12-hour shift.
3. 7 measurements exceeded 0.13 fiber/cc, which is the lower of the two proposed PEL adjusted for a 12-hour shift.
4. The slash (wet) saw operator's exposure was measured at 1.08 fiber/cc. This level exceeded 0.33 fiber/cc, the higher of the two proposed standard (adjusted for 12-hour shift). His exposure was 83% of the current standard of 1.3 fiber/cc (adjusted for 12hour shift).
4 D 001803
TABLE 1
RESULTS SUMMARY OF SEMI-ANNUAL ASBESTOS SURVEY
at . J-M Mfg. Inc., Denison, Texas
March 31, 1986 Galson Project #S6-350-00
Location Employee's Name
Operations
Exposure Sample Sampling Level
I.D. Duration Fibers/cc
1 Jimmy Lang
13' Utility Oper. 5756
254
2
Ed Heironimus
13* PM Tender
5757
246
3 Tommy Martin Gen. Worker
5778
279
4 Ray Terrell
13' PM Head Curer 5758
243
5 Cecil Bell
13' PM Curer
5774
239
6
Charlie Moore
13' Control Oper. 5771
250
7 Lewis Ives
13' PM Asst Serv
5766
270
8
Phillip French 13' Service Opr
5773
218
9
Charles Wilson 13 PM Stm Tank Opr 5759
263
10 Arlis Chambers Salvage Trk Driver 5763 259
11 Dale Kent
Willow Operator
12 Pete Turnbull Boiler Oprator
13 Bill Rogers
UPL Operator
14 Glen Weger
UPL Helper
15 James Walsh
UPL Inspector
5820 5775 5764 5768 5765
260 260 255 253 252
16 Roger Cam
Janitor
5761
306
17 Dock Dill
UPL Hydrotester Opr 5824
252
18 Raymond Hesse 13' Unit Leader
5809
248
19 Jeck Bartley
18000# Trk Driver 5776
249
20 Thurman Stanley MOA Operator
5777
246
21 Wilbur Greene Tool Room Opr
5762
246
22 Don Dutton
Molder
5787
168
23 Elliot't Brown Crew Leader
5792
167
24 Fredie Wright Utility Trk Driver 5803 216
25 Bill Williams Electrician
5793
125
26 Murel Abernathy Mechanic
5802
120
27 Jerry Bruce
Platform Trk Driver 5782
248
28 Jack Hansard
Sm Fork Trk Driver 5788
244
29 James Bush
Sample Plan Insp. 5815
240
30 Henry Coldiron In Process Insp. 5788 240
31 Lawrence Arnold Slash Saw Opr
5805
240
0.09 0.16 0.10 0.13 0 -15
0.16 0.21 0.11 < 0.02 0.02
0.19 < 0.02
0.09 0.03 0.09
0.05 0.04 0.06 0.03 0.04
0.05 0.04 0.03 0.02 < 0.03
0.04 0.08 0.03 0.08 0.03
1.08
* the locations correspond to those marked on Figure 1.
actual and estimated whole day time--weighted--average exposure level. 5 D 001804
Figure 1. Sketch showing employee workstations monitored lor asbestos. J-M Manufacturing, Inc., Denison, TX. March 31,1986. Galson Project ft S6-350-00. ((# ) corresponds to the codes as shown in Table 1.)
GALSON TECHNICAL SERVICES, INC.
OBSERVATIONS AND RECOMMENDATIONS
This survey was not intended to be a comprehensive industrial hygiene evaluation of the plant, but some of the observations made during the survey are summarized below with the corresponding recommendations:
1. Although exposure to the slash saw operator was below the current OSHA standard of 1.3 fiber/cc, his measurement warrants the use of a NIOSH approved respirator for protection against asbestos dust. At the minimum, a half-face respirator equipped with high efficient particulate aerosol (HEPA) filter cartridges is preferred.
2. During the survey, several workers were observed using NIOSH approved respirators equipped with dust pads for protection against asbestos dust. NIOSH has recommended that such dust pads not be used for this purpose, despite its continual "approval" as required by law. The dust pads should be replaced by HEPA cartridges.
3. The transparent shield at the local exhaust for one of the Universal Pipe Lathe (UPL) work stations was frequently missing, thus reducing the efficiency of the exhaust. The shield should be kept in place as much as feasible.
6 D 001806
Appendix I Sampling and analytical method
ASBESTOS (Summary of NIOSH P&CAM 239)
The sampling and analytical methods incorporated in this study were those recommended in NIOSH Method P&CAM 239 for the quantification of airborne asbestos fiber concentrations. The preferred index of asbestos exposure is the humber of fibers longer than 5 microns with a length to width aspect ratio greater than three to one, as counted on membrane -filters at 400-450X magnification by phase contrast microscopy. This method of analysis requires the use of specific procedures for the collection of the sample.
The principle of the sampling method is as follows. A known volume of air is drawn through a 0.8 micron pore size cellulose ester filter utilizing a personal sample pump. The pumps are calibrated prior to sampling using a calibrated, precision rotameter. Any particulate materials present in the sampled air impact on the filter. A portion of the filter is analyzed visually using phase contrast microscopy.
When analyzing the filter, only objects with a length at least three times the width and a total length of at least 5 microns are counted. The total number of fibers on the filter (with the above characteristics) is computed by determining the average number of fibers per unit area on a small portion of the filter and then multiplying this number by the total filter ar ea. The fiber concentration in air is then calculated by dividing the total number of fibers collected by the volume of air sampled.
Asbestos samples analyzed using the NIOSH method must contain a minimum of 10 fibers/100 fields to provide a statistically significant concentration measurement. A field is the area covered by the microscopy scale during the counting process. For samples with fewer than 10 fibers per 100 fields, a amaximum concentration is calculated using a nominal value of 10 fibers/100 fields and the volume of air sampled. Maximum concentrations are indicated by a less than (<) sign.
Thus, for comparison purposes, samples with fiber counts less than 10 fibers/100 fields are st atistically identical. For example, a fiber count
D 001808
of 5 fibers/100 fields is statistically identical to a count of 1 fiber per 100 fields, rather than being 5 times greater. In general, the precision of the counting method decreases with decreasing fiber concentrations. The coefficient of variation for this method is determined using Figure 1 in conjunction with the total fiber count reported on the laboratory data sheet. To determine the 955 confidence interval for the sample result, the reported value is multiplied by two times the coefficient of variation. Finally, note that this analytical method does not positively identify the fibers as asbestos.
2 D 01809
Appendix II Field Data Sheets
D 001810
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Appendix III Laboratory Data Sheets
Galson
Technical Sendees, Inc.
77 Bth Sheet Oakland. CA 94607
(415) 763-1677
laboratory data analysis
of 2
Environmental Sciences Division
Client: JM-Denison Date Sampled: NS 37mm cassette Porton Field = 0.0121mmA2
Job #: S6-350-00 Date Analyzed: 4/8/86
Client's Galson
I.D.
I.D.
Number of
Fields
Number
of Volume Fibers
Fibers
(L) per cc
Comments
5754 5756 5757 5758 5759
5760 5761 5762 5763 5764 5765
94896 94897 94898 94899 94900 94901 94902 94903 94904 94905 94906
100 NI 0 NA
blank
100 56.0 432 0.09
100 96.5 418 0.16
100 77.0 413 0.13
100 9.5 447 < 0.02
100 1.0
0 NA
blank
100 36.0 520 0.05
100 29.0 418 0.05 Overloaded filter
100 14.5 440 0.02
100 56.0 434 0.09
100 53.0 428 0.09
Submitted by: Approved by:
ANALYSIS METHOD: NIOSH P&CAM #239
D 001820
Galson
Technical Sanricaa, Inc.
77 8th Street Oakland. CA 94607
(415) 763-1677
laboratory data analysis
pg 2 of 2
Environmental Sciences Division
Client: JM-Denison Date Sampled: NS 37mm cassette
Porton Field = 0.0121mmA2
Job #: S6-350-00 Date Analyzed: 4/8/86
Client's Galson
I.D.
I.D.
Number . of
Fields
Number
of Volume Fibers
Fibers
(L) per cc
Comments
5766 5768 5771 5773 5774 5775 5776 5777 5778 5782 5788 5792 5793 5797 5798 5802 5803 5805 5809 5810 5820 5815 5824
94907 94908 94909 94910 94911 94912 94913 94914 94915 94916 94917 94918 94919 94920 94921 94922 94923 94924 94925 94926
94928 94927 94929
75 100.0 100 18.5 100 99.0 100 59.0 100 88.0 100 1.0 100 19.0 100 23.0 100 66.0 100 45.5 100 17.5 100 13.0 100 9.0 100 16.5 100 18.5 100 10.5 100 11.5
20 125.5 100 37.0
100 NI
84 100.0
100 48.5 100 22.0
459 430 425 371 406 442 423 418 474 422 415 284 213 286 408 204 367 408 422
0 442 408 428
0.21 0.03 0.16 0.11 0.15 < 0.02 0.03 0.04 0.10 0.08 0.03 0.03 < 0.03 0.04 0.03 0.04 0.02 1.08 0.06
NA blank 0.19 sample found uncapped 0.08 0.04
Submitted by: Approved by: -4-
ANALYSIS METHOD: NIOSH'P&CAM #239
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