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Here's an update on asbestos.
By O S. Bajhans, P.Eng., Occupational Haalth Branch. Occupational Health
. Engineering Services. Toronto, Ontario.
for asbestos was published in the U.K. by the Minister o( Labour.9 This was taken from the annual list of TLV's
There has always been an attempt published by the ACGIH:Iri 1965 The
on the part of scientists to establish a British pccupational Hygiene Society
hygienic standard for asbestos that is. | biologically most appropriate in limit
(BOHS) formed a Hygiene Standard Committee.' This committee, after
s ing the hazard. However, since nsbes- critical examination of ' the ACGIH
i tos was established as a human standards, recommended'the Use of
; carcinogen, it has been difficult to the ACGIH standard for asbestos for j establish a no-risk level, either for the time being, until they: have estab
! occupational exposure or non-occupa- lished their own standaW. "
; tional exposure. There is always some
In 1967, Cooper' observed that the
( small risk to health as long as there is ' TLV of 5 mppcf for asbestos rests on
; any airborne dust in the environ shakier evidence than most TLV's.
* ment. '
His chief argument was that a large
' Nevertheless, an allowable exposure proportion of asbestos fibres have
1 level must be set and defined by an diameters below the resolving power
: index based on the theory that expo of the light microscope used for
> sure u|> to pertain levels can be toler- Impinger counts and are therefore not | ated without incurring undue risks.. counted at all. He further reported
This article will olfer a critical review that asbestosis appeared in insulation
workers who were, exposed to con
centrations much below the time-.
weighted average of 6 mppcf.- Lea*
thart and Sanderson' also considered :
the TLV of 5 mppcf to be too high. In
January of 1968 the ACGIH issued the
following statement:
,
. "A" limit to. 6 mppcf, based on .
impinger samples counted by
light-field techniques is satis
factory to Control exposures to '
most forms of asbestos: Crocl- .
dolite, however, has been shown . .
. to produce- mesotheliomas ' in. . '
addition to the common ashes-.:,*:
totic inflammations. Since no
safe limit can 'be estalished for,,
this form of asbestos at this
time, until more definitive data -
are obtained, it.is recommended '
that workers exposed to croci- .
dolite be equipped with air-
of the existing and proposed occupa-
, tional and non-occupalional standards
for asbestos.
'
-.
OCCUPATIONAL STANDARDS The
occupational or work-environment
level is normally referred to as a
Threshold Limit Value (TLV) or
Time-Weighted Average (TWA).
These values refer to time-weighted
concentrations for a 7` or 8-hour work
day and 40-hour work week..They
refer to airborne concentrations under
which it is believed that nearly all
workers may he repeatedly exposed
day after day without adverse ef
fect.
In 1946, the American Goverrtmen-'
tal Industrial Hygienists proposed
that the TLV for asbestos dust be set
at 5 mppcf (million particles per cubic
foot), as determined from impinger samples.' This value was recom
0
mended by Dressen, Dallavalle, Ed wards, Miller and Sayers after a study of 5-11 employees in three asbestos
> :: viy- i's
V'ifj
Plgt l. Response to qhryeohi^e.'asbestos ;cxjj6s.ure: . ,\'-J
textile plants using ebrysotile asbes
\.\ i
' '
''
tos.1 In 1960 an occupational standard
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3H73
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i II it c* T at
OCCUPATIONAL HEALTH AND SAFETY
TEXWU 008505
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supplied helmet?.-
TEXTILE STUDY However, by this time, the Hygiene Standards Commit tee of the HOHS under the chairman.sht|> of Professor Lane bad already completed mi envmmmenUl and mmiteal alitfly at an asbestos textile factory in England, in which mvestigntitms were made of 290 of the men employed in the period of t933-l%ti.: The asltvslos dust concentrations to which different workers had been exposed varied from ! flbre/cc to 27
fthrvs/cc measured by the membrane filter (MK) technique in which the number of fibres greater than 5u in length were counted.
The problem of relating prevalence of aslxtslosis with concentration and with duration of exposure was re solved by assuming that the cumula
tive amount of asbestos remaining in the lungs from a given exposure is equally dependent on the dust con centration and on the duration of exposure to that concentration. Thus, the exposure of an individual was expressed its fibre-years/cc, that is the product of the average coneentra* lion during working hours and his , years of exposure. Rxposure ex pressed in this way w as compared to the prevalence of asbeslosis and a curve was developed." (Fiff.' tf.
One criticism of this curve was the use of a continuous scale starting at zero. Doses which give zero response are never, in fad, known with abso lute certainty since the sensitivity of a measuring instrument in limited. However* the main conclusion from the curve was that for an accumulated exposure of 10(1 fibre-veam/vc, it is probable that the risk of being affected, to the extent of having the earliest clinically demonstrated signs, is less than. T. That is, 2 libres/cc for 5U years, 4 libres/cc for 2b.years or Iff fibresAc for off yenra, 4 fibrosAx for 25 years or 10 librcs/cc for Iff years.
ACOIH In Httttlhc ACL Ml pm^tsvd a TLV of 12 fibres greater than fi um in length per cc by the MK teclmique or 2 tnppcf by the impinger technique. This was probably based on the work of Lynch, Ayer and Johnson* in asbestos textile plants where I mp|>vf (impinged was shown to be equal to 5.9 libres/ic. In 1970' the AttilH proposed a lower asbestos dost limit of 5 fibres>cr by tin* MK technique nd
eliminated the impingcr standard. ; However, this TLV remained on the
intended changes list until 1977 when it was first adopted as the TLV ami
. continues to be the one today. This j' TLV, if continued, would result in an j. accumulated exposure of 2f>0 fibre-
years/cc over 60 years and an extrapo should reduce the likelihood of die-
lation of the curve shown almvc would eases (malignant and non-malignant).
indicate that this would result in more resulting from exposure in excess of
than 2% risk of contracting asbesto 30 years with very long latent periods..
ses. . ' The US. Government published the
In 1972 NIOSH. recommended the following in the Federal Register, Vol.
following criteria for asbestos dust** 36, No. 234, December 7, UI7I."
"Occupational exposure to airborne
'The 8-hour time-weighted
asbestos dust shall be controlled so . average airborne concent ration
that no worker shall be exposed to
of asbestos dust to which em
more than 2.0 asbestos fibres per cubic . ployecs are exposed shall not
centimeter (cc) of air based on a count
exceed 6 fibers per milliliter
of fibres greater than 5 micrometers
greater than 6 microns in
(> 5 um) in length determined by the
length, as determined by the
membrane filter method at 400-450 X
membrane filter method at 400-
magnification (4 mm objective) phase
450X magnification (4 millime
contrast illumination,as described In
ter objective) phase contrast
Appendix 1; determined as a time- . illumination. Concentrations
weighted average (TWA) exposure . above 6 fibres per milliliter but,
for an 8-hour work day, and no peak , not to exceed 10 fibres per millil-
concentration' of asbestos to which. itef, may be permitted up to'a
workers are exposed shall exceed 10.0
total of 15 minutes in an hour
fibres/cc greater than $ um as deter
for up to 5 hours in an 8-hour
mined by a minimum sampling time
day."
of fifteen minutes," /;
. On June 7,1972" the OSH A promul- .
Along with the above recommends- gated a standard which limits the 1
tion the NIOSH. also, issued several worker exposure to an 8-hour time-
other statements:
weighted average . (TWA) of five .
asbestos fibres per cc of air; and the
7# ceiling limit of 10 fibres/cc. They also
mentioned that effective July I, 1976,
.*
; ICToncMtrat/on. <*
Category , -vypec
the 1972 rule would reduce the expo sure limit to an 8-hour exposure limit of 2 fibres/cc. Selikoff et al" criticised
Negligible / -Vvp.fWH v-:r; the standard on. the basis that the
Low/ ' \ Medium High. / .
,, MoO.'V-V*- ','.6v*r |0.O
fibres are made of fibrils 300 lo 350 Angstroms in diameter and cannot lie seen with the > optical microscope,
being far below the limits of its reso
(1) The standard is amenable
lution.
to techniques that 'are valid,
In 1973 the Hygiene Standard
reproducible and available to - Committee reviewed the 1968 ROMS
' industry and governmental
standard for chrysolite and recom
agencies. It will be subject to
mended that no changes be made at
review and will be revised as: the present time, but the standard be
necessary.
kept under review." They also re
(2) The recommended stan
viewed the information on the results
dard is designed primarily to
of human exposure to airborne mo
prevent asbestosis. For other
tile asbestos with animal experi
diseases associated with asbes
ments. They recommended that the
tos, there is insufficient infor
standards for amosite be the same as
mation lo establish a standard . those for chrysotile.
to prevent such diseases includ-
It was further recommended that -
mg asbestos-induced neoplasms
the following table (Table I) be used to
by any all-inclusive limit other
designate certain ranges o( dusti
than one of zero. Nevertheless, a
ness.
safety factor has been included
On October 9, 1975 the Federal
in arriving at the concentration
Register" proposed a standard of 0.5
level that will reduce the total
fibres per ce for an 8-hour TWA (or
body burden and should more
500,000 fibres per cubic meter) and
adequately guard against neo
likewise a reduced ceiling of 5 fibres
plasms.
per cc (or 5 million fibres per cubic
LATENCY A ceiling value of 10.0 meter) (or any period not exceeding
libres/cc that was not to be exceeded 15 minutes.
was included lo reduce the possibility IHPR The proposed standard did not
of the short-term heavy exposures to apply to the construction industry and
asbestos that have been reported to separate rulemaking lo revise the
cause mesolheliama. In addition, this asbestos standard for construction
NOVEMBER DECEMBER. 197/
TEX 3474
tq0NU 008506
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HOU 053385
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i
industry was plnnncd. The Insulation * Hygiene Progress Report" critically
' revieiVetl Hie. proposed OSH A stan dard and issued the following state
: ment:
contrast microscopy. Our study'' indi cates that it is not possible to monitor the levels at 0.1 fibres/cc reliably.
CANADA In'* Canada there is no uniform standard, all provinces have
air as determined liy tbe mem brane filter method of evalua
tion at KKVSOOx magnification using phase contrast illuminalion.
`'This recognition that the
their own asbestos standards. An
British Coin mbin "-The B.f.
construction industry is unique nttempt is made here to summarize Government have had a standard of 6
Is highly desirable. Earlier data
the provincial standards. -
mppcf (impingcr) for a tong lime.
on . the effectiveness of moni toring in the construction indus try {see Insulation Hygiene
' Quehci *--The standard to be ap- i However, they hnvc now their stan plied is 5 fibres/cc but the Beaudry .' dard apd recommended TtV of 2
commission has suggested a reduction ' fibres |>er cc greater than 5 urn in
Progress Reports, Summer
to 2 fibres per cc or the equivalent
length for chrysolite and 0.2 fibres/cc
1973), have shown that few dust
OnlnrtV-They followed the for crocidolite in tbe Second Draft
counts are ever taken in this
ACGIH recommendation until 1972 Amendments, Workmen s Compensa
segment of the Industry. Thus,
and then they lowered the standard to tion Board, industrial Health and
Specification of procedures is of
2 fibres/cc for chrysotile mainly due Safety Regulations, February. 1976.
; much greater importance here.
to the following:
They have also mentioned a ceiling of
Individual workers must be able
- (1) The U K. has been using
5 fibres/cc for 16-minute exposure.
to judge whether or not they are
this standard since 1971.
" This is it the ceiling level of 10 fibres/
working in a safe environment .
(2) The NIOSH criteria docu-
cc recommended by Ontario.
, on the basis of materials and'
ment recommended this limit
' Saakatchtimn.''--The province has a
methods rather than dust
(3) The toxicities of various. . TLV of 2 fibres/cc for all asbestos
counts.
types of asbestos is not well ' varieties.
"As much of insulation is now
understood and hence a built-in " ';Vot>a Sco(ia''-At present, the stan
asbestos-free, work practices for . installation of new material can
safety factor was needed,.
dard is 5 fibres/cc but new facilities
be developed that would lead to
| a time-weighted average expo-
| . sure less than that proposed in the new standard. With care,
.A
"-
..JSwifu**** .
* !j -
even ripout can be done safely*
but special precautions must be taken. Wetting techniques have
now been developed that would
`allow removal of asbestos to be
accomplished within the'pro- .
posed regulations."
.
2 fibre OSHAlnvited comments on i#v|rafutrafn v* sinn w,wi,iw ...i4'u *sy_ in y.\uqpn\iud ' 30^j8y ftV6[8 i ipproprialenesd and feasibility from'
he asbestos industry. On February 4,'
I[976" some 65 representatives from
Companies and trade associations repjesenting manufacturers and pro cesses of asbestos products in the United States participated in a meet-
phrARi-V' V - :
,'ri'Tt>ntrlo Min|8lry 6^*he EhylrohWanlkjf-&jpl4ridi guldeiln*.of.i`fg/m>
Fur crocidolite the standard is 0.2 will be required to meet the standard
ibg held in Washington, D.C. and fibres/cc. They also have a ceiling of 2 fibres/cc.
overwhelmingly endorsed that the "2 value of 10 fibres per cc for a 15-. The Working Group on Antonionis'*
fibre" level has been or can be . minute exposure.
recognized the documented and stis-
attained by.application of engineer , ii{5rrfa~-OmAprit 15,1975 Alberta peeled health hazards associated with
ing technology but the proposed "0.5 officially promulgated the following asbestos exposures and recommended
fibre" level is unnecessary, impractic- occupational health standards:
a uniform early acceptance of a
: aide and lacks medical justification,
(A) For asbestos dust or
maximum tolerable level of 2 fibres/
jin a letter-dated December 15,
fibre, all forths;. . the time-
ml., time-weighted average. The prac
1976*' to the OSHA, Dr. Finklea of the
weighted average airborne con
tical objective, however, should he to
N.IOSH recommends that the OSHA' . centrnlion. shall not exceed 2
reduce asbestos dust in the workplace
reduce the standard for occupational
fibres greater than 5 micro
to the lowest possible level.
exposure to asbestos to 0.1 fihroa per
meters in length per cubic centi-
Feasibility of 2 fibiysh-v Sta tnlunf
m Dr. Finklea said the previous : meter of air, as determined by
A standard should not he promul
' recommendation of a 2 fibres/cc was ` the membrane filter method of
gated on whether it is feasible to meet
designed primarily to prevent aslies- . evaluation at 400-450x magni
it or not. Almost anything is feasible
losw since insullicient information
fication using phase contrast
if it is necessary. However, it is a
then existed to establish a standard to
illumination.
'
worthwhile exercise (<> analyst* if I he
prevent aslwstos-related diseases such
(It) For asbestos dust or fibre,
standard is feasible. U should also ho
as. pulmonary, pleural and peritoneal
all forms, the maximum (ceil-, realized that 2 fibres/cc is a TWA over
neoplasms. The 0.1 fibre per cc recom
ing) airborne concentration
an 6-hoiir period. In other words some
mendation in based on lowest con-
shall not exceed 10 fibres
excursion during the period ran be
ccrStralion at which asbestos fibre?
greater Ilian 5 micrometers in
permitted, but the excursion is filmin'
enn he monitored reliably using phase
length per cubic centimeter of; to 10 lihres/cc. Now. if one suppose?
l'
I f * e'
I
40 J TEXWU 008507
Bilsom Propp-o-PIast
IIiiihIIc llie loiii'liL'st InitiiMic icq'uircnicuts wiIh liilsum I'mpp-o-l'lasl. No shaping ' tcquitcci, l<L\ul}-lo-ui'nr l'ropp-o-l'IasV;
tlisnosilhit' pltmsnrc piv-l'orliicd...
A thin phlstic flint uovci ink the , /'. ..
acoustical lihers inalnlitinsthe'ping
'
shape. .Severn! pnKulelh.ine plugs" '
Isiieli as I--A-K, Deci-Damp) icqmie
considerable nuihling aiul shaping
uhichcoukl easily imbedeolilniui-
minis into the plug mii face. I'ropp-o-
I'last plugs lenutin untouched aiul
' k irfM-Wi--'`3
hvuidiic. t'oml'i'i table, too, because" a
llie\ lit any si/e ear amt the minute . ' afi
pores in the plastic Him allow the plug .
%:lto hirallle. liennimiieal eiunigh In ' ^
loss away niter each use. I'lopp-o-Plast.
ins lIoDlilr.n.dViIsI 'pj oumsaobi 'lIeV ..
` a... ..
1
-h'
Bilsom for your comfort
llilsiml tnl u f o a I ioitaI!. IIn. i.. IIIINmIHinI oSun. ri.se t\.aolko il.lf.i.il,lust. im, .V, Ai 221191 I'Iidiic (70.1) 02(1,'t'tsu
'Mmm
that a worker is exposed to 10 fibres/ cc for 16 minutes he tfould he exposed to 1.7 fibres/cc for the rest of his shift, i.e. 6 x io 465 X 1.7 - 480 x 2.
Lcmcu et aP4 showed that more than 50% of the operations in textile operations were able to meet the 2 fibres/cc limit and eohtrol technology to meet the 2F/cc level existing in nil operations in the friction product industry. A 9tudy has been carried out in Ontario to determine the technolog ical feasibility of the 2 f/cc standard" as is the Beaudry Commission in Quebec.*" The Ontario report" shown that the level of 2 fibres per milliliter is technologically feasible in the five
major plants studied. COSTS Our studies in Ontario would
seem to indicate that the industry is well aide to bear significantly in creased control costs without enor mous dislocations in the industry. We enforce asbestos standard.as strict as that presently used anywhere in the world. At the present time, it would seem that our asbestos using indus tries are economically healthy and perfectly capatde of working under the necessary constraints imposed upon them.
Other Occupational Stn/ulnnl*
(1) The BOHS has recommended a level of 0.2 fibres/cc for rroi idolite. "
(2) The BOHS also gives the follow
ing alternative indices for chrysolite
asbesots." Respirable mass: -0.03 mg magnesium/m'
*
-0.04 mg SiO,/in*
-0.10 mg ash/m* --0.12 mg asbestos/m' Thermal Precipitator: 25 ppcc
greater than 1 um after incin
eration. Impinger: 10 ppcc
';
Uoyco Particle Counter: 2 ppcc
greater than 4 um.
It should, however, be realized that
the above standards refer to condi
tions in textile factories using chryso
lite asbestos and the equivalents may
not be applicable in other places. \
The joint ACGIH-AIHA Aerosol
Hazards Evaluation Committee9* af
ter reviewing various standards .in
cluding the mass concentration con
cluded that *'at present the only
practical way to determine fibre
concentration is by counting fibres
which have been mounted on a suit
able substrate so that they can be
identified as individual fibres.'*
environmental STANDARDS In 1-171 the Environmental Protection
Agency, U.S. Government proposed
emission standards concerning the
following:
(I) Emissions shall not exceed
those which would be emitted
from operations if proper engi-
neering control had Ihhmi in
stalled (i.e. fabric filter, cyclone
gas cleaning devicesl.
(2) Visible emissions of par
ticulate. (3| Spraying of asbestos.
(4) Use of asbestos for surfac
ing or resurfacing of roads.
The use of procedural standards am) visible emissions as the basis for eval
uation for compliance with the stan
dard are designed to minimize emis
sion to the atmosphere. At about the
same time the USA. through the Air
and Industrial Hygiene Balwratory,
California State iXqmitmcnt of
Health, asks that the total fibre count
downwind of an asbestos source not
exceed 10 times the total fibre count
upwind of that source. The Depart
ment of Environmental Protection.
State of Connecticut U.S. Environ
mental Protection'Agency. had the
problem under study, and required
only that there In* iio visible emission
or certain specified control equipment
must lie used, e g. a bughouse, high
energy serublwr, etc.
Ontario has an emission guideline
which is 5 inicrograms per cubic metre
averaged over n half boor at point of
impingement. This
- *,,
TEX 31'76 ..
^ TEXWU 008508
flic rnnronlrntion of asbes numerical relationship between the April' 6, 1973." The amendments
tos itvenigml over a half hour result* emission guideline and the ambient thereto were proposed October 25;
mg from the plume from any source, air quality guideline. The ambient air 1974.-
-
slack or vent. impinging on any recep quality guideline is the maximum The following are some of the high
tor. a school, shopping ceHlre, ground. concentration, averaged over 24 hours, lights of this new document as it
Hr., nl the lime when the wind Is to be found anywhere in the commu concent asbestos.
Mowing from the source directly nity..
(1) The "no visible emissions"
Imvnrd the receptor.
Table II summarizes some of the air
clause for the waste disposal of
Since wind direction is variable and quality standards tii'force today.
asbestos materials remains in .
since more titan one source may The Final National Emission Stan
effect
V
impinge on n given receptor at one dards for Hazardous Air Pollutants-
(2) Asbestos mills are exempt
time, the emission guideline is devel Asbestos and Mercury, promulgated
from the requirement to wet
oped to enrumpu&t these variables in by the U.S. Environmental Protection ' tailings when disposal site lem
such a way that, if every source meets Agency, were published in the Federal, . tperatures are below 15* F.
the emission guideline, the ambient Register of October 14, 1975s* and are
. (3) Only asphalt concrete
air quality guideline will not be effective as of that date. Initially the . ` manufacturing plants that use
exceeded. Thus, there is no direct standards appeared m the Register of
commercial'asbestos are af
fected.
. . (4) Local exhaust ventilation
systems may be used during
Have confidence in your test results:
accuhaler 808"
i . certain renovation operations.
' (6) Containers of asbestos
.waste may display either an
EPA or an.. OSHA warning
label: '
;
. -
the accurate personal sampling pump
V {6) Clarification is given of . the definitions for "planned
' renovation" and "emergency re
novation" operations.
"
' 1 . (7) Wastes generated by op
- erations that use sprayed-on
materials containing less than
1% of asbestos by weight to
insulate or fireproof buildings,
structures, pipes and conduits
are not covered by the new
ruling, ohas
REFERENCES
1. Rajhans, G.S.: Fibrous Dust--Hs Mea
surement and Control, CfMM Bulle
i tin.. pp. 900-910, August. 1970.
2. Dreesen, W.C.. DaHavaHe, J.M. Ed
wards, T,l. Miller, J.W. Sayers. R.R..
Accuhaler 808 Personal Sampling System {including pump, orifices,
1.
tube holder end calibration kit.l
. Easom, H.F. and Trice, M.F., "A Study of Asbestosls In the Asbestos Textile Industry," Pub. Health Bus. No. 241, <
PiffMW vO'un'i* n'eaturptvipnt
* Eii'lv ulibralcd
'.< RrMfenp. 1 oli/rne.
Pplrpti'inn t)i|lilblCf. rml Ofltcr
o><r*m<r nilmancts
* Controlled inhalation
Will not iterate when flow
hhterteU
'
.
unttveriliablr
i: |;
ulH
LOiV. 9rf;i'Sl9l,lr flow 'He:
r.r. lo 96 cc min
MESA approve! no. 2G 3026 .
lor Mcthrme Atmospheres
BASEEPA approval
and
CEflCHAR approval no 776504X
| 1 Voi use w(fi Charcoal, 5hc#
for Hyrltojci* Almosplreres
OH low flow Onnior
THifs -
For additional information and your hee copy of the Charcoal Tube User
Guide, cat! or write:
*
Washington, D C . 1938. 3. Addlngley, C.G.: Asbestos Dust and
Its Measurement, Ann. Occ. Hyg., 9, 2., 1966. 4. Committee of Hygiene Standards of ! the British Occupational Hygiene So* clety: Hygiene standards lor chrysotlle asbestos dust. Ann. Occup. Hyg.
11:47-69, 1968. 5. leatharl, O.I.. and Sanderson. J.T.,
"Some Observations on Asbastosis."
Ann: Occup. Hyg., 6: pp. 65-74,
1983.
MDkk SCIENTFIC,INC.
HOU 053387
8C^6u5seify*^vnfkcRicdiggee. anonOC^Phcre 3&x> 4250 te*e>r-?2-dOWAiDA'PWD
6. "Threshold Limit Values of Airborne Contaminants," Adopted at the 30th Annua) Meeting of the American Conference of Governmental Indus trial Hygienists, St. Louis. Missouri,
MDkSului(kmv SCIENTIFIC tUKJLTD. reu'dcwnlncHst 86Cot>naml?tJ WmborneOcrtel.BH2I7PQ England
Phone 202-87206 tee* 4?22<?C'M!La?-0-
May 13. 1968. 7. "Hygiene Standards lor chrysolite
asbestos dUsl," Ann. Occup. Hyg., Vol. 13, pp. 7-15, 1970. ` 0, Roach. S.A.. "Hygiene Standards for
Asfrewne." Am*. QxC fry? 7-j?
IX dpi 7-1X i970
TE* 3177
x'rr* .'f.n-xrv
TEXWU 008509
9. Lynch J.R., AyBr H.E., Johnson D.C.:
The Inler-relallohshlps ol selected
asbestos exposure Indices. Amer.'
Industr. Hyg. Assoc. J. 31:598-604,
1970. .
.
10. Criteria for e Recommended Stan
dard for Occupations! Exposure to
Asbestos, U.S. Department of Health,
Education, and Welfare, Public
Health Service, Health Services and
Mental Health Administration, Nation
al Institute for Occupational Safety
and Health, HSM # 72-10267. Wash
ington. 0C, 1973. 11. Federal Register, 36,234. pp. 2.342-2,
343. Dec. 7, 1971.
t2. federal Register. 37,22,142-11,144,
Oct. te. 1972.
13. Setlkolf, I.J., Hammond. E.C. and H. Seldmsn: Cancer Risk of Insulation Workers In the United Slates Biolog
ical Effects of Asbestos, pp. 209-216.
international Agency for Research on Cancer, Lyon, 1973. 14. Anonymous. Review of Ihe Hygiene
' Standard for Chrysolite Asbestos Dust. Ann. Occup. Hyg., Vol. 16, p. 7. 1973.
15. federal Register. Vol. 40. No. 197,
Thursday. Ocl. 9, 1975.
16. Anonymous. New Asbestos Standard Proposed, Insulation Hygiene Prog
ress Report. Vol. 7, No. 3 arid 4.
Winter. 1975.
17. Asbestos, p. 8-90, Feb. 1976. IB. Federal Register, Vol. 42. No. 130,
Thursday. July 7, 1977. .
19. Rajharis. Q.S.. Q.M. Bragg and S.
Morton: Asbestos Exposures in On tario--A Review, -Presented at the
A.I,H. Conference New Orleans. May
24. 19R
20. Camite d elude Sur la Salubrite dans Hndustlre de I'amianle. pp. '262-285. April 1976.
21. Anon.. Asbestos Data Sheet. Occu pational Health Protection Branch; Ontario. Ministry of Health. August 1976.
22. Rajhans. G.S. and J.R. Assad: Engi neering Aspects of Asbestos Oust Control. Ann Arbor Science Publisher
Inc. Ann Arbor (under Publication).
23. Report ol the Asbestos Working
Group, Health and Welfare Canada. Feb. 15. 1976.
24. Lemen. R.A., J.M. Oement and R.E.
Seiler; New Asbesloa Standard-- Feasibility of Compliance within Se lected Asbestos Industries. NIOSH Internal Report. 1972.
25. (Unpublished Report). Occupational Health Protection Br., Ontario Minis try of Health. August 1976.
26 Background Documentation on Eval
uation of Occupational Exposure to Airborne Asbestos. ACGIH-AIHA Aerosol Hazards Evaluation Commit
tee, Am. Ind. Hyg. Assoc. J. 36:91.
1974.
-27. Anon.: Asbestos As a Hazardous Contaminant II. Ont. Ministry ol Envi
ronment. Jan. 1975.
28. Anon.. Asbestos, p. 14, Nov 1975.
You can tackle many OSHA noise measurements
withthis one instrument
GenRad's 1982 Precision Sound-Level Meter and Analyzer puts a Variety of OSHA-type noisemeasurement capabilities in the palm of your hand: ;
1. precision soundJevel measurement 2. octave-band analysis 3. peak (impact) noise measurement
Just turn a knob and flip a switch to change functions. You don't need plug-in filters or other add-on accessories;
i Precision microphone for IEC end ANSI Type 1 Measurements. It's removable lor remote mike positioning.
Make octave-band
f measurements bv se
lecting 10 bend! Irom 31.6 Hz lo 10 kHz.
z Digital display allows
quick: accurate., error-
free reading.
; The analog meter is calibrated linearly in 1<!B steps for easy re
' reeding. .
. Set digital display lo
hold feadout ol a spe-
cific event or to up- ` '
date end hold the high-
*. est leyet measured. Or
set lo track the ambient
levels.
.'
,, For precision sound- ` level measurements, select weighting. A for OSHA. or B. C. or Met response.
' Select measurement ' range from 30 lo 140 dB m four 60-dB steps.,
Select meter response.
' slow of peak (impact!
for OSHA. Fast and Impulse also select able.
> Recharge batteries here.
The 1982 is your single-instrument answer for OSHA and general-purpose noise measurements. Request complete details from GenRad, 300 Baker Avenue. Concord, Massachusetts 01742; (617) 369-8770
HOU 053388
GenRad
,1* 3'7'
NOVEMBER 'DECEMBER. 1977
For more facia chela,17 on card.
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