Document jNBbB57pN7VwzdK51Djr47p5y
DUST EXPOSURES DURING THE /CUTTING AND MACHINING OF
ASBESTOS/CEMENT PIPE ' ADDITIONAL STUDIES
Prepared for
The A/C Pipe Producers Association
1600 Wilson Boulevard
Suite 1308
~
Arlington, Virginia 22209
Prepared by
Equitable Environmental Health, Inc 2020 Mil via Street
Berkeley, California 94704
December 15, 1977
EEXHIBIT
INTRODUCTION
On March 16, 1977, Equitable Environmental Health, Inc., submitted a draft -
report to the A/C Pipe Producers Association which provided quantitative data
on dust exposures during .field operations in which sewer and pressure pipe
were subjected to a number of typical field cutting and machining operations.
A final report on the above'was completed in July 1977, and the results have been incorporated in recommendations for work practices in the handling of A/C ^ j
'pipe../- V .... ,
On July 12, 1977, the Association requested additional studies of dust
i Vs
exposures involving other field operations. These also included a quantita
tive estimation of potential exposures to quartz. '
T.'7.
. ' / ' STUOY DESIGN & OPERATIONAL PLAN . ~
' . I-
Determination of airborne asbestos fiber concentrations. Airborne fiber
concentrations were determined during the following operations:
(1) Unloading pressure pipe at work site ,, .
(2) Laying pressure pipe in trench
V.
(3) Cutting operations
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a. Cutting with manual saw (pressure pipe)
b. Cutting with snap cutting equipment (pressure and sewer pipe)
c. Cutting with abrasive disc wet (pressure and sewer pipe)
(4) Machining operations a. Cutting and machining with Doty tool (pressure and sewer pipe)
b. Use of tapering tool (air duct pipe)
c. Machining differing sizes of pressure pipe (4", 8", and 16") with manual lathe
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2
(5) Hole cutting a. Use of drill and rasp (pressure and sewer pipe)
(6) Tapping operations a. Dry tap with Mueller J (pressure and sewer pipe) b. Wet tap with Mueller B-100 . (pressure and sewer pipe)
(7) Coupling removal (i.e. removing pipe from line) .a. Hammer^and chisel (pressure-And.-sa.ver-,pipe) . .; i
It was not possible to set up a cutting operation with a water-cooled masonry (radial arm) 'saw, or to remove pipe from a line with a sabre saw.
Determination of quartz.. Samples of total and respirable dust integrated
over a number of operations were collected and analyzed for quartz.
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\ . METHODS
Each operation, when performed in the field, is of short duration compared to an 8-hour workday. ..Consequently, the OSHA ceiling standard, intended to cover short periods of relatively intense exposure, would be more likely to be exceeded than would be the 8-hour time weighted average (TWA) standard. A sampling period of 15 minutes is regarded as suitable for determining "peak" or ceiling exposures while at the same time obtaining an adequate sample for analysis.
Most of the cutting and machining operations took less than 15 minutes-, some required less than a minute. In these cases it was decided to perform the same operation several times during the sampling period. The times will be indicated.
CTD030237
For each operation, except as otherwise indicated, three replicate '
short-term breathing zone samples were collected for the operator and for
his helper. ' ..
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7. . Vi-'
Simultaneously, longer-term personal samples were collected on the-:
operator and his helper,, over a period of two to three hours and covering more
than one type'of field operation.' : Also, integrated area samples were collected
at a site approximately 15 feet away and downwind (if there was air movement),
Other area samplers located:.! to 5'feet from the field operations were used
to collect:total dust and respirable dust by'weight. Samples' used'for total
dust were changed every 4 hours; those for respirable dust every 8 hours. Three
such samples were used to determine quartz content. Background samples were
collected before and after each day's operations.
:-
Air .samples wefe collected on 37-millimeter diameter, '!).8 micron pore
vsize Millipore cellulose ester membrane filters in accordance with OSHA aTid
NIOSH recommendations. They were all "open-face" (with the cover of the filter
cassette removed) samples'. .Personal sampling pumps were operated at flow rates :
ranging from 1.6 to 2 liters per minute. The pumps were calibrated by the soap
bubble technique before use.' Both area and personal (breathing-zone) samples
were taken.; In the latter, the pump was attached to the worker's belt"and the
filter clipped to his lapel near his face. Figure 1 in the July, 1977 Report
illustrates worker and helper with samplers in place. Figure 2 in the'same
report shows the test site with area samplers located near the operation.
Asbestos fiber counts were done by an experienced and accredited technician,
following OSHA and NIOSH methods. The same technician was employed who had ~ '
worked in the earlier A/C pipe study. Briefly, the analytic procedure consisted
of rendering the filter transparent with a high viscosity solution of membrane
filter material in a mixture of diethyl oxalate and dimethyl phthalate. The
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asbestos fibers which lie on the surface of the filter are counted with a phase
contrast microscope at 400x magnification. The count area was delineated with
a Porton graticule. Only fibers exceeding 5 micrometers in length were counted.
The laboratory examined 100 microscopic fields or counted 100 fibers, whichever
came first. Fiber identification depended upon a particle having an aspect
ratio of at least 3:1 and having approximately parallel sides. No attempt was
made to identify individual fibers mineralogically in view of the known chryso-
tile and crocidolite content of the material under-examination. Fibers which
appeared not to be asbestos were noted when seen. No estimate was made of the
number of fibers less than 5 micrometers in length, nor the number in the electron
microscope range. Samples were stored for such studies if they should appear
desirable at some later time.
; .
It should be emphasized that estimates of fiber concentrations below
5 fibers/cc are subject to increasing lack of precision, and that those below
0.5 fibers/cc have a wide margin of error, often being based on the observation
of very few fibers. For example, in a 15 minute sample, one fiber observed
per 100 fields is equivalent to 0.05-0.07 fibers/cc, which is the approximate
lower limit of detection for this sampling period. Although counts are reported
as calculated, to two decimal places, small differences in counts in these ranges
should not be overinterpreted. A zero count merely means that the count was too
low for any fibers to be seen in 100 fields and is consistent with a very low
concentration of airborne fibers. Samples for gravimetric dust concentrations
were weighed in the laboratory of EEH. Quartz analyses were performed by
George Clayton Associates.
Performance of study; As in the previous study, all of the operations were carried out on the premises of Pilot Mfg. Co., a manufacturer of A/C pipe:equip-
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merit in Torrance, California, except for unloading and placing in trench which were done on a job site in Alameda County, California. A workman experienced in the use of the tools performed the individual operations, with a helper pro vided by EEH. EEH independently purchased the necessary sewer pipe and pressure pipe for cutting and machining from a local supply house. All pipe was 8 inches in diameter unless otherwise specified. As before, no engineering dust control or local ventilation was utilized, except-when this was built into the equipment being used (as was true for some of the tests using the Doty tool, and when wetting was added to the use of the abrasive disc).
GENERAL DESCRIPTION OF OPERATIONS
The study, exqept^or unloading and pipe-laying operations, v/as carried out
ring the period October 1-15, 1977. Mrs. Barbara Kawahara was the industrial
lygienist, and she was assisted by Mr. Jerry Flanery of the EEH staff. The
feather during the period was in general overcast, with clearing skies in mid-
orning. Temperatures during the test periods ranged from 16-21 C (60 to 70 F).
here was relatively little breeze in the mornings, with gusty breezes up to
or 10 mph in the_afternoons_.___ __
...--
Housekeeping. In order to minimize contamination of the test area with
st and scrap, a commercial vacuum cleaner was brought in to maintain a clean
rk area. Unfortunately, it was ineffective because of a worn gasket, and blew
sible dust from its exhaust. It was necessary to wet down the area periodi-
ly and sweep up loose scraps and dust.
CTD030240
DETAILED DESCRIPTION OF OPERATIONS AND SAMPLING TIMES V I
(1) Unloading. This was done with a palletized load, using a fork-lift (Figures 1 & 2). The pipe was arranged on 4 foot pallets, 8 per bed, plus miscellaneous short lengths and couplings. It took approximately 15 minutes to unload a two-bed truck. Up until three or four years ago, it had been ' customary for the pipes to be loaded individually by being rolled down skids. To unload a two-bed truck in this manner took about 2 hours. '
For this operation a single 24-minute personal sample Was collected on the fork-lift operator while pressure pipe was being unloaded.
(2) Laying pipe in trench.' The operation which was studied involved ' trenching, laying pipe, and filling simultaneously (Figures 3-5). One worker remained in the trench at the forward end of the pipe. The second worker worked both topsffle fhd in the trench. He attached a clamp to the pipe, lubricated the end, then got into the trench to help guide it into place for coupling. Two 1-1/2 hour-samples were collected by personal samplers placed on the two workers
(3a) Cutting with manual saw. (Figure 6). Due to the inability to pro cure an appropriate bow saw blade, a standard hack saw was used with a hardened steel blade. The blade was changed before each run. Sampling times ranged from 12 to 15 minutes, during which time it was possible to cut about one-half way through the 8" pressure pipe. This tool was not used with sewer pipe.
(3b) Cutting with snap cutting equipment. For this portion of the study a Wheeler Chain Cutter (Model 2990) was used.; It has cutting discs mounted on a chain which is wrapped around the pipe (Figures 7 & 8). The action'is controlled hydraulically by an operator who can stand as far as 10 to 15 feet from the pipe being cut. The set-up between cuts took about two minutes. Pumping to build up pressure required about 15 seconds. Five to 8 cuts were
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made during each sampling period; the average panged from 14 to 16 minutes
for sewer pipe and 13 to .16 minutes for pressure pipe.
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(3c) Cutting with abrasive disc, wet. A gasoline-powered abrasive disc
saw (Stihl) with a 10-inch carbide blade was used (Figures 9rll). Four 1/4
inch diameter plastic hoses were mounted on the housing of the saw, :'two on a
side as shown in Fjjgure 10,".in accordance with TAC Ltd. blueprints provided by . '
AACPP. These were connected to a manifold to which was attached a hose deliver
ing
water/at a rate 'of 2 to 3 gallons per minute'..; -
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A preliminary run was with .'a saw.that proved to be
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underpowered,
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.,
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requiring ?
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18 minutes for .two-cuts'. ,,:.With a^more powerful ..saw (1-1/2 hp motor) a _cut could
be completed in approximately 1-1/2 minutes!/Two to 3 cuts were taken per sample', :; the sampling periods having been reduced to 3 to`6 minutes after an initial test
sampling period of 17 minutes had led to overloading of the filter with .dust. ' j7"
lis test, was run on pressure pipe only.
-
(4a) Cutting and machining with Doty tool. The Doty tool (Figures 12-15) ..
has two operating stations, one for cutting, and one for machining. " It has
three operating modes: dry, dry with shroud, and wet with.shroud. The .last ' -
two modifications were to reduce dust generation and dispersion. During tests
of the tool in the dry mode with shroud and wet mode with shroud, a plastic
hag was piaced over the blade to reduce dust (Figure 13).
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..'
All cuts were made wet, because a diamond blade is used. A fine spray of
/ater is directed across the blade during operations. About one-half'minute
s required for a ,single cut.
' . i'. .t. v:. -
Machining was done dry with no shroud, dry with shroud; and wet with
hroud. Again for the wet mode, a fine spray was used. Machining'took about -
minute. Most of the sampling time involved moving pipe. . Use of the Doty
ioI is essentially a one-man operation, a helper being needed only to move
lrge pipes.
CTD030242
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Two to four cuts and two to four machine operations were completed per
sample cycle. Sampling time was reduced from approximately 15 minutes to
approximately 10 minutes for the dry mode because it raised visible dust. It
was observed that on the dry mode with shroud tests, visible dust was released
during bevelling. It is suggested that a gasket or some other seal would be
helpful in preventing this.
Sampling times recorded for the use of the Doty tool, wet, for pressure
pipe were 10 to 11 minutes and for sewer pipe 9 to 15 minutes. For use of Doty
tool, dry with shroud, with pressure pipe the sampling times were 13 to 17 minutes, .' and for the "sewer pipi~i2 rb~T4 minutes7 For the use wet with shroud,'Yi to 18 ? \
minute sampling times were employed for pressure pipe, 12 to 16 minutes for
sewer pipe.
. . ".
, '
(4b) Use of tapering tool with A/C air duct pipe. Test of the tapering
tool (Figure 16) was limited to 10-inch A/C air duct pipe, which has a thick-
ness of approximately 1/4 inch. Its operating principle is similar to that of
the manual field lathe. Sampling times ranged from 14 to 22 minutes which
included one-cutr and one tapering operation.
(4c) Machining with manual lathe on differing sizes of pipe. In order
to determine whether or not the size of pipe had a detectable influence on dust
production, a manual lathing operation was carried out on pressure pipe of 4-inch, I
; 8-inch, and 16-inch diameter (Figures 17 & 18). For the 4-inch pipe there was .
one cut and one machining for each sample, set-up requiring about 3 minutes, cut
requiring about 3 minutes, secopd set-up about 4 minutes, and machining about
8 minutes, the sampling times for the three replications being 13 to 21 minutes.
' For 8-inch pipe, again one cut and one machining was carried out for each
sample, the set-up requiring about 3-1/2 minutes, the cut about 2 minutes,
second set-up requiring about 2 minutes and machining about 10 minutes. The .
CTTX02A3
replicate samples ranged from 19 to 21 minutes. For the 16-inch pipe there was one partial cut per sample; each sample included some machining and some
cutting. The set-up required 3 minutes, the cutting about 12 minutes, the second set-up about 2 minutes, and machining about 20 minutes.
--
(5a) Hole cutting with drill and rasp. For this operation (Figures 19-21) 5/8-inch holes were drilled on the pipe in a circular pattern of about 6 inches in diameter, after which the central portion was knocked'out with a hammer.and j". the rough edges smoothed with a rasp. The operator used the exhaust .^air from the drill to blow off excess dust (Figure 22)Although the practicV.'of "blowing"
asbestos-cement dust isnot recommended, it was used in this instance to duplicate i
"worst possible" work practices or tool performance characteristics.:.%The drilling _
took a long time to complete, so that only about 3/4 of the circumference was
'
finished in one sampling period...'.`Therefore, some samples did not include the-
hammer and file steps. -Sampling times for pressure pipe ranged from 16-to 24
minutes, for sewer pipe from 17 to 21 minutes.
./ ..
';V.; .
(6a) Tapping operations with Mueller 0 tool. (Figure 23). The Mueller J
tool is used for tapping pipes, not pressurized,at the trench top or in the
^
trench. In the latter case, a hole is dug to expose the pipe, but for the -'c'..-.
test, a pipe which had not been installed was employed. A manually operated \_. .
tool was used, which cuts a hole and threads it. Two one-incn holes .were cut
-
per sampling period. Sampling periods for pressure pipe were 14 to 19 minutes. -
(6b) Tapping operations with Mueller B-100 tool. The Mueller B-100 tool
(Figure 24) is used for tapping pipes already in line, usually those under
pressure. It has a pressure chamber'to keep the water from flowing out during
the tests. I\t the recommendation of the local Mueller representative, this
chamber was filled with water to simulate "wet" conditions during the tests. There
were two holes cut per sampling period; the sampling times were 14 to 19 minutes.
CTD030244
(7a) Removal of coupling with hammer and chisel. For pressure pipe, a
?
hammer and chisel were used to make a longitudinal trough in the coupling
(Figure 25). When this had been completed, a crowbar was used to separate the
'
coupling. For pressure pipe this took about 22 minutes, one coupling being
J
removed per sample. With sewer pipe, the same procedure took about 10 minutes
>
per sample. It was soon found that by placing the chisel midline on the coupling,
one or two sharp hits would split the coupling, a procedure which took only 10- !
30 seconds per coupling. . For sewer pipe, 3 to 4 couplings were cut per sample, ?
the major portion of the sampling time being during moving pipe and securing it i
to supports. '-;
> : ,.:v `}
- Order of tests. Availability of equipment and efficient use of pipe and
manpower led to the actual tests being carried out in an order different from .
. that summarized in the foregoing outline. The order of testing was as follows:
' Monday, (Tctober 10, 1977
Cutting with snap cutting equipment, pressure pipe (3b)
Cutting with hack.saw,, pressure pipe (3a).... (;;
;
Machining with manual lathe, 8-inch pressure pipe (5c)
Machining with manual lathe, 4-inch pressure pipe (5c)
Machining with manual lathe, 16-inch pressure pipe (5c) Hole cutting with drill and rasp, pressure pipe (5a)
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*P
Tuesday, October 11, 1977 : .
V
Coupling removal, hammer and chisel, pressure pipe (7a)
Tap with Mueller J, pressure pipe (6a)
Tap with Mueller B-100, pressure pipe (6b) .
Tap with Mueller B-100, sewer pipe (6b)
..
Tap with Mueller J, sewer pipe (6a)
Use of tapering tool on A/C air duct (4b) Cutting with snap cutting equipment, sewer pipe (3b)
.
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Wednesday, October 12, 1977
Cutting with hacksaw, sewer pipe (3a) ,... I
;v
Hole cutting with drill and rasp, sewer pipe (5a)
Cutting with abrasive disc, wet, pressure pipe (3c)
Removal of coupling with hammer and chisel, sewer pipe (7a)
Thursday, October 14, 1977 ' T.
''
rCutting and machining with Doty tool, dry, pressure pipei(4a)
^Cutting and machining with Doty tool, dry, shroud, pressure pipe(4a)
: ' - Cutting and machining with Doty tool, wet,'shroud, pressure pipe (4a)
Cutting and machining with Doty tool, dry,'sewer pipe (4a)
_ Cutting and machining.;with Doty tool, dry,shroud,'.sewer pipe (4a)
- Cutting and machining"with Doty tool, wet,'.shroud, sewer"pipe (4aj
Friday, October 15, .1977
:r /Cutting with abrasive disc, wet, pressure pipe (3c) - : / /
. Cutting wtth abrasive disc, wet, sewer pipe (3c)
.
Testing at Bay Area site Unloading pipe at site 0) Laying pipe in trench ;(2)
Integrated long-term samples were taken as shown in the tables of
results.
RESULTS
The short-term or peak exposures during the operations studied are shown in Tables 1-6. Integrated personal samples analyzed for asbestos fiber concen trations are shown in Table 7. Table 8 summarizes integrated area samples, which were studied for asbestos fiber concentrations, total dust, respirable dust, and quartz content, as shown. None of the respirable samples, i.e. samples collected with a pre-filter cyclone to remove large non-respirable
CTDO30246
i
particles, showed a measurable amount of dust sufficient for quartz analysis. Table 9 summarizes background levels.'
DISCUSSION
Background levels, as in the previous study, were at the limit of sensi
tivity for the volumes of air and the'methods employed. Ranging from below the
level of detection to 0.07 fibers/ml, they .indicate low concentrations, similar
to those found in many earlier studies.
Short-term or peak exposures. All operations that were studied produced `
airborne concentrations far below the current short-term standard of .10 fibers/ml
or the proposed short-term standard of 5 fibers/ml, except for some operations '}
using the Doty tool and operations using the abrasive disc saw. Some operations
using the Doty tool, particularly when used dry, although below the permissible
concentrations for short-term exposures, would if continued over an 8-hour day, "
exceed the permissible time weighted average of 2.0 fibers/ml. It is, of course,
unlikely that use would be continuous.
-
v;
The abrasive disc saw, even.when used wet, produced unacceptably high `
concentrations of airborne fibers, averages ranging from 10 to 65 fibers/ml.
It is believed that use of water to cut down dust with this machine could be
improved upon. Because the hose was attached to the housing and the latter
could be rotated with respect to the handle of the saw, the water was not invar
iably directed to the cutting area. It was observed also that dust was generated
within the pipe during the cutting and would exhaust from the ends of the pipe, and
this could not be reduced by water applied to the outside of the pipe. Also,
although the outside of the pipe was thoroughly wet, as the cut proceeded, the
disc would generate heat and dry an area on either side of the blade. It is
CTO030247
-ecornnended that water be applied through a fine spray, spread over a wide field, .0 that nozzle placement would not be critical. We do not feel that the wet-
rutting modification employed in our tests was designed to cover all conditions
if tool positioning and usage, therefore the possibility of effective dust re- .
luction with a proper method of wetting should not be ruled out.
. The quartz analyses, which employed x-ray diffraction methods which would
.
e used by OSHA and most industrial hygienists,showed more than 5% quartz in . .
ach of the total dust samples that were analyzed, specifically 5.7%, 9.0J, and
5.4%.'\:The threshold limit value, i.e., the permissible time-weighted average
ror total quartz-containing dust, is 30 ma/m^ . Therefore, in the three "
v
. . . - % quartz + 3 :
'V'.r-
amples measured, "the range of TWA's would have been from 1.6 to 2.6 mg/m^. ;
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o concentrations this high were reported in the integrated samples collected
>
-irig the current ^tuiffes. The high levels reported in the previous survey v ->7,-:.
ere peak, not integrated samples.
'
CTD030248
Summary and Conclusions
14
Determinations were made of airborne asbestos fiber concentrations, total
dust and respirable dust concentrations, and crystalline silica concentrations
during a number of field operations used in the cutting, machining and instal lation of asbestos-cement pipe. These were designed to supplement studies re
li
17
ported in 1977, which showed that potential asbestos exposures during most operations were well below current occupational health standards, but that one tool, the abrasive disc saw, resulted in unacceptably high concentrations of fibers. In addition, short term concentrations of total dust suggested that if crystalline silica content was high, permissible levels might be exceeded.
E s
'J if
H e
The additional studies included a test of the abrasive disc saw with an
attachment for wetting the area being cut, tests in which concentrations of
crystalline silica were determined, as well as tests of several operations not
previously studied. Specifically, the following operations were included:
(1) unloading of pressure pipe at the work site; (2) laying pressure pipe in
a trench; t3) cutting pressure pipe with a manual saw; cutting pressure and
sewer pipe with snap cutting equipment; cutting pressure and sewer pipe with an
abrasive disc, wet; (4) cutting and machining pressure and sewer pipe with a
Doty tool, with various modifications, wet and dry; use of tapering tool on air duct pipe; machining differing sizes of pressure pipe (4-, 8-, and 16-inch), with
ii
il
a manual lathe; (5) hole cutting pressure and sewer pipe with drill and rasp;
(6) dry tapping pressure and sewer pipe with a Mueller J tool, wet tapping,
pressure and sewer pipe with a Mueller B-100 tool; and (7) removing coupling
from pressure and sewer pipe with hammer and chisel.
8' -
&
All operations that were studied produced airborne concentrations of asbestos
far below the current short term OSHA standard of 10 fibers/ml (> 5um in length) and none would have exceeded a time-weighted average of 2 f/ml or even 0.5 f/ml
I'.
I
: v'.,.......... ' the abvjilva
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CTD030249
15 if continued for a full working day except for (1) the abrasive disc saw and (2) some operations with the Doty tool when used dry. The abrasive disc, even when used wet, resulted in fiber concentrations ranging from 10 to 65 f/ml. It was concluded that better design of the wetting method was essential. The con centrations observed with the Doty tool, dry, were below short-term standards, and would have exceeded the time weighted ayerage of 2 f/ml only in the unlikely event of being used continuously over a full work day.
Integrated total dust samples contained 5.7%, 9.0% and 15.4% quartz. This meant that permissible time-weighted averages would have ranged from 1.6 to 2.6 mg/cubic meter. The only integrated sample that exceeded the current OSHA standard was that collected during use of the abrasive disc saw.
These additional studies confirm that asbestos-cement pipe can be cut, machined, and installed without exceeding current and proposed OSHA standards, but that use of proper tools and adherance to recommended work practices are essential.
CTDO30250
; . Table 1
Airborne Fiber Concentrations During Unloading of Pressure Pipe and Laying Pipe in Trench
Ooeration
Duration, -(min) '
Fibers/ ml
Unloading pipe Laying pipe
24 * . / ' ';' J921
0.03 :o
Laying pipe Background
v'7.,.90
'/ - '
' ' 32
_ 0.02 .. -0
*Below detectable limit
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17 CTD030252
Airborne F iber Concentrations During Machining Operations
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S-'
a
0tr-3j o
<u
aS.- 'co
o
L03
<
.O t= uZ
u
4(Uo-O>
03 c
OCL
O--' l-- C
p r--
R3
t-
3
Q
to oo co OOiHhCsj
H cm on oj
cn 3" -h co HCJHH
oooo
N CO w N ^HHCVJ ooo o
r-H O O tH *--< r"H
to H pH i-H
Nmo
in CM CM NIOCOC3
chhoh
CO CM 03 CO LO O CM O *--1 CM *-H
GO Ot LO p-H rH CM pH CM odoo
rH O O rH rH rH
-
lO CO r--1 I-H i-H
co co
* -
O*
c u
C r-- T- O
C JO o
o o 1--
r- ia
P
2! >> *P
. o o
aj CL
Q 03
>> u
ol
c jr o 1- 4->
o-pa
.c ro <U s: -o 13 o u JC CO
* >J co
c fa
V
03
s: *o
L to
.p
c CJ
18 I B 5
CTD030253
19
ne Fiber Concentrations
anual Lathe
` *'*:/v**-`.
' - - _
-
v*.'!
'v 'Hel per ^ v; ; rt\.
-.Duration '.Fibers/
t-.....
,
. y v .
..
(min) V"-.ml ;
J
fr
i.. **- *s .. * * * k' .*
18 r v 19
0
`21. 0.05
rX-u^rirlo.oz
- ' vv -- V. . fttTi T
'
liv-cr.
;.' -Y`2207*-;-V-^7'
, ... ...
20 v-5?S'0.24 v ` % * ^ / - ' 21 -H-^'0.07
- -.r^--p.l3
r7 *?.
C|)f ?
. 18
0.05
-15 0.07
` ' ,20 ' *' 0.05 * '* - Or06
;
' '
- . Table 5
Airborne Fiber Concentrations During Use of Tapering Tool with A/C Air Duct Pipe ' .
tool . r duct
Operator.-
.Duration Fibers/
(min)
ml
- 14 , 0.28 ' ,
23 ; 0.13 .
. . Helper -
.Duration .Fibers/
' (min)
ml
. '14 ^o`06
.22 .0
20 i.
rranm ttM h
-
CTD030255
in
U OJ J=t B
U . IOJ CL
<u c a= o
-
<a E
S~-- tu 3 . L -0 CL
: ** !<u
CJ
.' U
O
00
J<U- I--
J=t E.
U-
* in in co
CM fHo -(
OO o
w LO CO
. o. o o o
o oo
oooo
CM CO o *o
o . oo
21
hnco 1 . tnvoio
cm hh _ 'r.--< -- (H
co rs. co m
CoM o-i CoM CoM
I-*. CM CO
Oo *o- o oo
> r** io
o oo oo
cvirs
io *'
. 0 o o '1*0-
.o o
o
cn c
4- n3
. <U q5 -- c: o
.r-
4D oo "T3
o /a
o
<C fO u>
-- i-c
4- o
C T- . cu 4-j
O ixj
. C S- ' o oj C_J CL
O . *-
* <U 03
.
^ -Q C .
* .. ul a.
CL
cj iq
;-'ch So .*. 'jQ i. ; S- .. r-- =c
j'groi-j ' "f?
CL' .
<u - IIo--. i-O-. *r to
* 53
in in OJ U O f
E
S- --
_ -
:3 ..o
;
'/
</i saj i-- JQ E
So 4J (O . iCJ - CL o
-
Lju
c o-~> T- C 4-> 1-- iSd_--E--3
OCO **--HH tOo
* O pO O
:*' tOo G-- lOflrOs
O OOo
^ CO N CM i
fcin rx ci ` , - * -
';
CO *5" CO CM *-4 *--4 CO CM
oooo
.. t .
` to cn
oo oo
w
in o
*5j- Ol to Whh
^ r*' *"H --4
' . /
* o. : in
ta cc
* "a cc o <X3 *r* 4-> Oif-- 3 C 1-- U r* *r" OJ +-> So. +j a o3
O -C 4J
OJ -r-
o
c (O CJ
IE
C J CJ s:
-M O *r-- Sx J-
<u CLr-- 1X3 t-- 1-- aj
3 L.
*3* O IO CO *-H CM O H
oooo
:
CJ IO o H-* *"* O f--I
oooo
cn co
/ in id
*-<HH / . - ;v--CM f-- f--i
i". -< ; ,, oi o w o ,, t-< -i ..- cm <n to m
o U o o * w-* o o0 om o
Cl c--o4 M*---*
V. CcMm tr-oH rin--i
CTD030256
: * ... .
; '
id CJ s:
'' ..
- -v.. ,.*
c * *IO w '
------- <u ' -VI -
o
o -4
JO 1 +4 CO f-- 5 s_
CJ
CL#-- (rt i-- 1-- CJ
4_) 3 /*
s *.**,> CJ .`r.fA*0 * - v; E *a
.<u c CS co - . '.Ol t, C CJ
. * '* **" E V'1 E
^ . V CL nz ' 3 3: r'
:.- -
!* . '* '
_*
CJ JJ
u_
in in <T3 r-- CD
s r--1
CJ c ,o
m 3
Table 7
-b.
Integrated Personal Samples Covering Successive Operations
Average Peak ' Counts
, Integrated Sample Counts
f
Operation
Operator Helper
Fibers/ Fibers/ ml ml
Operator
Helper
. Duration Fibers/ Duration Fibers
(min)
ml
(mini
ml . f
lap cutting pressure ick saw, pressure .nual field lathe 8" .
nual field lathe 4"
nual field lathe 16'* -
le drilling
.
-- .'* y\* '-- 1^'.
upling, hammer and chisel eller j, pressure .
eller, B-100, pressure
eller, B-100, sewer
iller-0, sewer . ering tool., air-ckct
ing, snap-cutting
.l.i '
.ting, hack saw, .sewer e drilling, sewer_ asive disc, wet, pressure* .
piing removal, sewer .
y tool, dry, pressure y tool, dry, shroud, pressure t tool, wet, shroud, pressure / tool, dry, sewer * tool, dry, shroud, sewer ' tool, wet, shroud, sewer
sive disc, wet, pressure sive disc, wet, sewer
0.02 0.01 0.03
0 0.11 0.13
I#-
250
0 0.02 0.22 ;
0.02 0.06 0.06.
0.3 0.05 0.11 0.06
:o.i '
0.07 0.13
' 0.0 i
1 JI- 228 J t. . ' * i . .
V 275
-j
. 0.06 ' 0.18
0.04
0.03 0.02 0.05
1 h . ' '226
J
0.18 0.23 4.30
0.08
0.13 0.79
1 V ... 264
J
0.06 0.10 J 132
1.90 1.29 0.21 3.83 0.23 0.20
2.23 0.18 0.27 0.29 0.09 0.05
`'I .
t-
237
65.02 49.15 42.1 10.22
\
6?
0.02 0.08
0.05 .
250 0.11 j
. w" . t?l -- .trj 229 '0.02 5 '/
279 0.04 |
*' 0.06
;'.__ ^ 226~
* ...
- ** ' * .. 0.02
6
0.34 . 253
0.14 . .\ "
0.05
178 0.03
0.35
237 -.0.26
5.84
74 5.80
or underpowered, only one test tried.
CTD030257
^ Table 8 Integrated Area Samples Covering Successive Operations
: v.Operations
:tting Tpressure . * w cutting, pressure
fi el d 1 athe '8" "Pressure.' - v- \
field lathe 4" pressure field lathe 16" pressure
ill ing :
' .. -v /
.* .
removal, hammer lisel , Mueller 0, pressure . Mueller B-100, _ ire'
Mueller B-100, sewer
Area Samples ;
v -#*` *
Asbestos Fibers '-".Total Oust
Duration .Fibers '-Duration v?^ ' (min) ^ml ,:v~(min) - ino/r -
- '/fa.'* ' 'Quartet
: Content , v; u **.
v-*-.V *
251 0.57
0.33 ,`iS
234 ; 0.04
235
286 0.02 290' ;0.34
Mueller 0, sewerpipe tool with A/C air ipe ting sewer pipe
y 225
0.02
233 0.00
cutting, sewer pipe ling, sewer pipe ive disc, pressure
removal, sewer pipe
272 0.12.
}u
0.02 . 191
0.79
- 5.7%
CTD030258
Table 8 Cont'd Integrated Area Samples Covering Successive Operations
24
Operations
Cutting and machining, Doty dry pressure
Cutting and machining, dry, shroud, pressure
Cutting and machining, wet, shroud, pressure
Cutting and machining wet, shroud, pressure
Cutting and machining dry, sewer
Cutting and macWnirt^ dry, shroud, sewer
Cutting and machining wet, shroud, pressure
Abrasive disc wet, pressure pipe
Abrasive disc wet, sewer
pipe
Area Samples
Asbestos Fibers
Total Oust
Duration Fibers Duration
(min) ml
(min) mg/nT
\
238 0.03
240 0.20
'i
l
80 3.83
821.66
f
J
Quartz j Content I
Not Deter-
mined
i [ I
*
if
15.4S
.1
CTD030259
* i '* -
v-^'25
*
Table 9 '. '
' - . i.*.-.:;
j,.
A'l rborne Fiber Concentrations Before and After Operations. ,
'^...(Background Levels)
-
. >.*.'
.-
-
.*r... \
v;>- '
-
'
Date and Time
. , 7' . Duration
. Fibers/
'
-
. Si. *
*'' fr.v...
^-wv.
(min)
' ml
. ^ .5 Xlv.*}-?'? --
October 10, 1977 am
55 ' 17.1'f 0* -
"ii-
- October 10, 1977 pm ` *
October 11, 1977 am
w.
r * ; ` N-^v .*
' 0.02 " . 0.07
_\ ' %:/. ' rWM?M
October 11, 1977 pm ,SU7:~V85 ;>.<: o.o , ;::'V
..
i 7 ^ : v
-f-vL"
i-?
October 12, 1977 am :r2r-rC^'5'-M-^.-472.--^0 01
October 12, 1977rpm ^^fr'^r75o ->.
..'r.--5
\
* ' ; ' -V' * v
October 14, 1977am'Afc':129 :<
.' October 14, .1977 pm
91
o.oo2 'r V-
*..:
<*$-} r- '
`
*>. s .. V '.v.-
-V
:.n&S&L ,
"#a?
'
October .15, 1977 am <
October 15, 1977 pm
7^:72.>;:;-:o.oi !'
-30
'll n
.? '
.......... ...
*- s?: . , v *
- ..--..- .-'* ...v' r'..r. .v ** -
'Below detectable .1 imit-
v.: :v.\`. '
.' r.*
.*
k
r.- ?. -
- -.`4' ~ ,-'r_.::
' . ~ i. ' "'-v. . -v .' V . r,r
-v,-r:.-.'
* ';
. .'i. .
:<am ' */ * w::
v-
r * ."'v L * `
- rw *-*
' *-: : rV rS-lK.-
. ~r. =; ,:,
.
v.
.'
.**'
> '
-
. '. .
.'* . ' -
. .V4- .T'S*' . *.-.<?> "
;
; /.:7..V..--... . ....- ?r---jf.r ".
. 7/--, v'
'
- . " V.*
V-.l ' " : Vr'l*:*-*
CTD030260
26
FIGURE 2. Transporting 8-inch pressure pipe from truck to trench.
C7D030261
<7
CTD030262
. 28
i
i
E
[
FIGURE 6. Cutting with hack saw
S'
CTD030263
FIGURE 8. Hydraulic control of snap cutting equipment... . CTD030264
V
FIGURE .9. Abrasive ifet/cutting.
disc
saw
with
hoses'for
FIGURE 10.". Abrasive disc saw with hoses for wet cutting
".w':dV-----..... ....
CTD030265
f i
r
i
I f B I
' FIGURE 13
t
Doty tool, cutting, with bag around blade.
C7D030267
"33
FIGURE 16. Tapering A/C air duct.
C7D030268
34
FIGURE 17. '.Use of manual lathe on 16-inch
; pressure pipe. ; '
i
FIGURE 18. Use pressure pipe.
of manual
lathe on
4-inch
f f l
I
'fi
H
CTDO30269
35 CTD030270
36
CTD030271
g
n
37
FIGURE 23. Use of Mueller J tool. /
.FIGURE 24. Mueller B-100 tool.
CTD030272
38 FIGURE 25. Removal of coupling with chisel.
CTO030#3