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^ SERVICES REPORT Wausau Insurance Companies
2000 WESTWOOD DRIVE WAUSAU, WISCONSIN 54401
E. W. Ostrander, Treasurer 1 Bird and Son, Incorporated Washington Street East Walpole, 'Massachusetts
02032
! CONCERNING
! Aero Drive Shreveport, Louisiana
April IS, 1980
dP
PLAINTIFF'S EXHIBIT BIR-158
REPORTED BY
H. S. Freshwater, environmental health engineer; and T. D. Hennings, safety consultant; an March 3, 1980
PERSONS CONTACTED ' Frank Burris, manufacturing manager Michael W. Bottoms, personnel manager Larry Batey, project engineer Huey Haire, plant .engineer
REPORT SUMMARY
ENVIRONMENTAL HEALTH ENGINEERING SERVICE
This survey was made at the request of Mr. Michael W, Bottoms, personnel manager, to determine the concentrations of silica dust, asbestos fibers, and fibrous glass to which selected employees are exposed during normal plant operations.
Air samples were collected and ventilation ma
nents were made.
The following comments and suggestions arie^bj sed Upon the results of this survey:
Air Sampling Program
1. Airborne asbestos samples wsm coQgcted on 0.8 micron membrane filters,, mounted open face downward riN&ne breathing zones of the workers. The
samples were subsequently returned to the laboratory (AIHA Accreditation Number 34) and analyzed using phase contrast microscopy. During the survey,
the operator in the cement plant used the old mixer.
Xfre results given in Table I show that all the samples were well below the OSHA^ttHnistration permissible exposure limits. Since respiratory protection
001106
This report covets only conditions and prac tices observed and considered at the time of this call. It is not intended to indicate that any hazards are adequately controlled or that such conditions or practices meet the requirements of any applicable federal, state, or local law, regulation, or ordinance.
If you have any comments or questions concerning this report, write to G. B. Lemke, Vice-President, Safety & Health Sendees.
Consultative safety and health services are available (o all policyholders, and we en courage you to contact your servicing safety-
BIRD 014946
E. W. Ostrander Bird and Son, Incorporated
-2-
April 15, 1980
was worn at these operations, actual exposure concentrations would have been lower than the sample results.
An analysis of a bulk sample of talc showed It to be nonfibrnug.
2 Three airborne silica samples were collected on preweighed, five micron pore-sized membrane filters using the respirable mass sampling techniques described in "OSHA Standard Method for Respirable Gravimetric Dust Sampling." The samples were then\returned to the laboratory, reweighed, and examined by X-ray diffractometry. to determine the amounts of dust and the percentages of free crystalline silica present.
The results of the air sampling program are shown in Table II together with
the OSHAdministration permissible exposure limits as calculated from the silica analyses (29 CFR 1910.1000, Table Z-3).
Sample number 3 exceeded the OSHA Standard, being almost five tlinea t-hw permissible exposure limit.
As indicated in sample._nimbeg_4, the bulk, sample of talc was also analyzed and found to contain J?iveVpagcentfarmca.
3. Two additional personal samples for fiberglass were collected on preweighed, 0.8 micron cellulose acetate filters mounted open face downward in each ' worker's breathing zone. The samples vere returned to the laboratory, reweighed, and checked for fibrous glass using polarized light microscopy and X-ray diffraction.
The results given in Table III show that no fibrous glass was detected In either of the samples. However, both samples exceeded the OSHAdministration permissible exposure limit for nonasbestosform talc dust of six milligrams per cubic meter (29 CFR 1910.1000, Table Z-3). This-value (six milligrams per cubic meter) is arrived at by converting the 20 million particles per cubic foot standard to a mass concentration based on the equivalence of six million particles per cubic foot equalling one milligram per cubic meter respirable mass and respirable mass equalling 50 percent total mass.' This conversion is described in the "Threshold Limit Values for Chemical Substances and Physical Agents in the Workroom Environment for 1979," by the American Conference of Governmental Industrial Hygienists.
Using X-ray diffraction, approximately one percent free .crystalline silica was detected in each sample which further increases the hazard potential. Since the method used was for the purpose of determining fiberglass exposures. additional samples would be needed for a more accurate assessment of the silica and talc exposures at these locations, if needed.
001107
BIRD 014947
E. W. Ostrander Bird and Son, Incorporated
-3-
April IS, 1980
The dust exposure is primarily from the handling of talc during "thread-up" operations. Total dust concentrations varied from 0.98 milligrams per cubic . meter to 27 milligrams per cubic meter, depending on periods of felt break down. Results given in the table are average values or time weighted averages.
Ventilation Survey and Controls
4. Ventilation measurements made in the cement plant showed inflow velocities
at the old mixer of SO. feet per minute (fpm) at the hood over the hag
storage barrel and 500 to 700 fpm (from right side to left side, respectively) at the bag cutting/^nd dumping station. At the new mixer, inflow velocities
of 25 to 50 f
sre detected at the bag barrel and 300 to 380 fpm at the
cutting and dunfping station. These values can be compared to the recommended
rate of^SO tfpm. Reducing the open areas at the bag dumping hoods would
increase ventilation effectiveness further.
Duct velocities of 500 fpm and 350 fpm were measured at the bag barrel hoods of the old and new mixerjivrespecti'rely. These rates are well below the minimum transport velocity ofL3.50ff/f'pm which is needed for self-cleaning systems.
5. Additional ventilation measurements were made at the hood over the top drum roll of number 9 section, FSPM number 1 line. Inflow velocities ranging from nondetected (less than 25 fpm) at the front and up to 80 fpr* at the side of the hood were measured with the front lid up. When the lid was lowered, corresponding rates of 50 fpm and 100 fpm resulted.
To Improve dust control, it is advisable that the lid be lowered at all times, when passible. Further enclosing the roller by reducing the open area on the sides would also improve the ventilation control.
6. As mentioned in comment number 3, the main dust exposure to the drv felt men on FSPM number 1 line seemed to be from handling the talc during "thread-up." During the survey, the talc barrels were located against the wall causing the workers to have to carry handfuls of the talc a long distance to the rolls. If possible, the barrels or smaller containers should be located as close to the rolls as possible to reduce the talc handling time and distance. Since a lot of talc is spilled during the hand carrying process, this change would also seem to reduce the amount of talc that is wasted.
7. It is believed that some of the dust to which the slate man is exposed is from the talc on the top drum roll on number 9 section, FSPM number 1 line. Better control of this dust source- (a3 previously described) should help to reduce his dust exposure. However, a substantial dust exposure comes during the sweeping of slate and from leaks in the material handling equipment.
001108
BIRD 014948
E. W. Ostrander Bird and Son, Incorporated
-4-
April 15, 1980
Any steps that could be taken to minimize the need for sweeping and shoveling would help to reduce this exposure. Wetting the slate prior to sweeping/ shoveling would also reduce the amount of dust becoming airborne.'
Material handling equipment needs to be as enclosed as possible and also be provided with exhaust ventilation to reduce escaping dust. Such dust sources include material transfer points, screens, conveyors, and bucket elevators. Enclosed are Prints VS-304 through VS-307 from "Industrial Ventilation" (Committee on Industrial Ventilation, Post Office Box 16153, Lansing, Michigan) which illustrate typical ventilation design specifications for these sources.
Until the dust exposure can be adequately controlled through engineering means, the slate operator should wear a NIOSH approved respirator for protection against silica dust.
8. ' A vacuum cleaner is used in the cement plant to clean up possible asbestos dust. To minimize the recirculation of the dust back into the workplace, you should check and make sure that the vacuum filter is of the high efficiency (HEPA1 type and replaced with this type if not.
9. A respiratory protection program should be written and implemented for the employees who wear the protective devices. Items to be Included in the program were discussed and are given in the OSHA Regulations (29 CFR 1910.134). For example, for respirators to be effective, they need to be properly fitted. maintained and cleaned, and stored.
Specific- respiratory and other requirements for asbestos exposures are given in the OSHA Regulations (29 CFR 1910.1001, Asbestos).
The aforementioned comments and suggestions, except for analytical results, were discussed with the gentlemen contacted (as aforementioned) at a'meeting following the survey. The analytical results were given to Mr. Bottoms by telephone on March 14, 1980. Please let us know if we can be of further assistance.
HO 74
cc: Robert C. Roby (11) Frank Burris
001109
BIRD 014949
TABLE I
CONCENTRATIONS OF ASBESTOS
* - Bsgiau u ........
__ .. --
b
Bird and Son, Incorporated Shreveport, Louisiana March 3, 1980
Sample Number
Sample Location
1 FSPM number 3, dry felt man(3)
2 FSPM number 3, dry felt, man(3)
3 Cement plant operator during cutting and dumping of bags(3)
4 Cement plant operator. time weighted exposure (3)
Found Fibers/cc(2)
OSHA AcceDtable(l) Fibers/cc(2)
0.2 <=--------- ---------------- 2
0.17-------------------------- 2
0.15 <------------------------ 10(4)
,
0.07--------- ----------------- 2
(1) (2) (3) (4) '
OSHA Acceptable - Title 29 Code of Federal Regulations Part 1910, Subpart Z, Section 1910<1001, Asbestos.
Fibers/cc greater than 5 mu - Asbestos fibers per cubic centimeter of air greater than 5 microns in length.
Operator wore respiratory protective device.
Acceptable Celling Concentration.
OOiiio
BIRD 014950
TABLE II
CONCENTRATIONS OF SILICA DOST
Bird and Son, Incorporated Shreveport, Louisiana March 3, 1980
Sample Number
1 2
3 4.
Sample Location FSPM number 1, foreman ESPM number 1, coater
operator FSPM number 1, slate man
Talc, bulk sample
Percent Silica
5 12
5
Found mg./M3(2)
0.4 <-
0.3 -t3.4 --
OSHA Acceptable mg./M~*(2) 1.43
-1.43 ->0.71
OSHA Acceptable - Title 29 Code of Federal Regulations Part 1910, Subpart Z, Section 1910.1000, Air Contaminants, Table Z-3.
(2) mg./M^ - Milligrams of contaminant per cubic meter of air.
001111 BIRD 014951
TABLE XII
CONCENTRATIONS OF FIBROUS GLASS
--------\ . i i
Bird and Son, Incorporated Shreveport, Louisiana March 3, 1980
Sample Number
Sample Location
1 FSFM number 1, dry felt man
2 FSFM number 1, dry felt man
Total Dust mg,/tj3(3) 16.23 7.81
Found Fibers/cc(2)
NIOSH Recommended Value(1)
Fibers/cc(2)
.ND(4) ----------- --;----------- 3
ND(4)~d--------------------------- 3
(1) Fibrous Glass Acceptable Airborne Concentration, as recommended by NIOSH "Criteria For a Recommended Standard...Occupational Exposure to Fibrous Glass."
(2) Fiberglass fibers per cubic centimeter of air equal to or greater than 10 microns in length and a diameter equal to or less than 3.5 microns.
(3) mg./M^ - Milligrams of contaminant per cubic meter of air.
(4) HD - None detected.
001112
BIRD 014952
SPECIFIC OPERATIONS
O
5-33
Duet velocity - 3500fpm minimum O -150 cfm/sq ft face Entry loss 0.25 VP
MANUAL LOADING
*BELT SPEED
VOLUME
Less than 200fpm - 3SOcfm/ft ofbelt
' width.
Not less than 150 cfm/ft
of opening.
Over 200fpm -
500cfm/ft ofbett width.
` Not less than200cfm/ft of opening.
AMERICAN CONFERENCE OF GOVERNMENTAL INDUSTRIAL HYGIENISTS
BIN a HOPPER VENTILATION
date /~72 I VS-304
001113
BIRD 014953
5-34
INDUSTRIAL VENTILATION
Alternate exhaust point
Additional ventilation for hopper, bin, or screen See VS-304, VS-307
For casing only O s 100 cfm/sq ft casing cross
Section Duct velocity -3500fpm minimum Entry loss - i-0 VP or calculate
. from individual losses
Preferred exhaust point
Tcke -off at top for hot materials, at tap and bottom if elevator is over 30 ft high, otherwise optional.:
Beit speed
Volume
Less than 200 fpm -- 350cfm/ft of belt width. Not less than /50cfm/ft of opening
Over 200fpm --500cfm/ft ofbelt width. Not less than 200cfm/ft of opening
AMERICAN CONFERENCE OF GOVERNMENTAL INDUSTRIAL HYGIENISTS
BUCKET ELEVATOR VENTILATION
DATE
t-66
VS -305
001114
BIRD 014954
SPECIFIC OPERATIONS
5-35
L Conveyor transfer less than J' fait. For greater fat! provide additional exhaust at tower belt See
3 below.
3. Chute to belt trensfer and conveyor transfer. greeter than 3 foil. Use addih'ona! exhaust at far dusty materia1 as follows: Belt width 12''-36" 0=700 cfm above 36, 0=1000cfm
2. Conveyor to elevator with magnetic separator.
DESIGN OATH Transferpo/hts:
Enclose fa provide 150-200 fpm indraft at all openings
Minimum 0=350cfm/ft belt width for belt speeds under 200fpm
- 500 cfm/ft belt width for belt speeds over 200fpm and for magnetic separators
Duct velocity =3500 fpm minimum Entry loss = 0.25VP
Conveyor belts: Cover belt between transfer points Exhaust at transfer points Exhaust additional' 350 cfm/ft of belt width at 30' intervals. Use 45* tapered connections Entry loss = 0.25 VP
Note:
Dry, very dusty materials may require exhaust volumes 1.5 to 2.0'times stated values.
AMERICAN CONFERENCE OF
GOVERNMENTAL INDUSTRIAL HYGIENISTS
Detail of belt opening
CONVEYOR BELT VENTILATION
DATE
!-72
VS-306
001115
BIRD 014955
5-36
INDUSTRIAL VENTILATION
FLAT DECK SCREEN
Q -200 cfm/sq ft through hood openings, hut not less than SO cfm/sq ft screen area. No increase for multiple decks
Duct velocity - 3500 fpm minimum Entrytoss - 0.50 VP
Complete enclosure
. Screen-
45nun slope
A--------------- 7
i
i i i i
i
i i i
i
_ _ j-.
//\ Hopper f
Oversize
/
CYLINDRICAL SCREEN 0 -iOO cfm/sq ft circular cross section of
screen; at least 400 cfm/sq ft of enclosure opening Duct velocity - 3500 fpm minimum Entry loss = 0.50 VP
AMERICAN CONFERENCE OF GOVERNMENTAL INDUSTRIAL HYGIENISTS
DATE
SCREENS
1-64
VS-307
001116
BIRD 014956
BIRD 014945