For the past 20 plus years, NIOSH has subscribed to a carcinogen policy
that was published in 1976 by Edward J. Fairchild, II, Associate Director for
Cincinnati Operations, which called for "no detectable exposure levels for
proven carcinogenic substances" (Annals of the New York Academy of Sciences,
271:200-207, 1976). This was in response to a generic OSHA rulemaking on
carcinogens. Because of advances in science and in approaches to risk
assessment and risk management, NIOSH has adopted a more inclusive policy.
NIOSH recommended exposure limits (RELs) will be based on risk evaluations
using human or animal health effects data, and on an assessment of what levels
can be feasibly achieved by engineering controls and measured by analytical
techniques. To the extent feasible, NIOSH will project not only a no-effect
exposure, but also exposure levels at which there may be residual risks. This
policy applies to all workplace hazards, including carcinogens, and is
responsive to Section 20(a)(3) of the Occupational Safety and Health Act of
1970, which charges NIOSH to ". . .describe exposure levels that are safe for
various periods of employment, including but not limited to the exposure
levels at which no employee will suffer impaired health or functional
capacities or diminished life expectancy as a result of his work experience."
The effect of this new policy will be the development, whenever
possible, of quantitative RELs that are based on human and/or animal data, as
well as on the consideration of technological feasibility for controlling
workplace exposures to the REL. Under the old policy, RELs for most
carcinogens were non-quantitative values labeled "lowest feasible
concentration (LFC)." [Note: There are a few exceptions to LFC RELs for
carcinogens (e.g., RELs for asbestos, formaldehyde, benzene, and ethylene
oxide are quantitative values based primarily on analytical limits of
detection or technological feasibility). Also, in 1989, NIOSH adopted several
quantitative RELs for carcinogens from OSHA's permissible exposure limit (PEL)
update.]
Under the new policy, NIOSH will also recommend the complete range of
respirators (as determined by the NIOSH Respirator Decision Logic) for
carcinogens with quantitative RELs. In this way, respirators will be
consistently recommended regardless of whether a substance is a carcinogen
or a non-carcinogen.
Old Policy
In the past, NIOSH identified numerous substances that should be
treated as potential occupational carcinogens even though OSHA might not have
identified them as such. In determining their carcinogenicity, NIOSH used the
OSHA classification outlined in 29 CFR 1990.103, which states in part:
Potential occupational carcinogen means any substance, or combination or
mixture of substances, which causes an increased incidence of benign and/or
malignant
neoplasms, or a substantial decrease in the latency period between exposure
and onset of neoplasms in humans or in one or more experimental mammalian
species as the result of any oral, respiratory or dermal exposure, or any
other exposure which results in the induction of tumors at a site other than
the site of administration. This definition also includes any substance which
is metabolized into one or more potential occupational carcinogens by mammals.
When thresholds for carcinogens that would protect 100% of the
population had not been identified, NIOSH usually recommended that
occupational exposures to carcinogens be limited to the lowest feasible
concentration. To ensure maximum protection from carcinogens through the
use of respiratory protection, NIOSH also recommended that only the most
reliable
and protective respirators be used. These respirators include (1) a
self-contained breathing apparatus (SCBA) that has a full facepiece and is
operated in a positive-pressure mode, or (2) a supplied-air respirator that
has a full facepiece and is operated in a pressure-demand or other
positive-pressure mode in combination with an auxiliary SCBA operated in a
pressure-demand or other positive-pressure mode.
Recommendations to be Revised
The RELs and respirator recommendations for carcinogens listed in this
edition of the Pocket Guide still reflect the old policy. Changes in
the RELs and respirator recommendations that reflect the new policy will be
included in future editions.
APPENDIX B
THIRTEEN OSHA-REGULATED CARCINOGENS
Without establishing PELs, OSHA promulgated standards in 1974 to
regulate the industrial use of 13 chemicals identified as potential
occupational
carcinogens.
2-acetylaminofluorene
4-aminodiphenyl
benzidine
bis-chloromethyl ether
3,3'-dichlorobenzidine
4-dimethylaminoazobenzene
ethyleneimine
methyl chloromethyl ether
alpha-naphthylamine
beta-naphthylamine
4-nitrobiphenyl
N-nitrosodimethylamine
beta-propiolactone
Exposures of workers to these 13
chemicals are to be controlled through the required use of engineering
controls, work practices, and personal protective equipment, including
respirators.
See 29 CFR 1910.1003-1910.1016 for specific details of these requirements.
Respirator selections in the Pocket Guide are based on NIOSH policy, which
considers the 13 chemicals to be potential occupational carcinogens.
APPENDIX C
SUPPLEMENTARY EXPOSURE LIMITS
Aldehydes (Low-Molecular-Weight)
Exposure to acetaldehyde has produced nasal tumors in rats and laryngeal
tumors in hamsters, and exposure to malonaldehyde has produced thyroid gland
and
pancreatic islet cell tumors in rats. NIOSH therefore recommends that
acetaldehyde and
malonaldehyde be considered potential occupational carcinogens in conformance
with the OSHA carcinogen policy.
Testing has not been completed to determine the
carcinogenicity of acrolein, butyraldehyde (CAS#: 123-72-8), crotonaldehyde,
glutaraldehyde, glyoxal (CAS#: 107-22-2), paraformaldehyde (CAS#: 30525-89-4),
propiolaldehyde (CAS#: 624-67-9), propionaldehyde (CAS#: 123-38-6), and
n-valeraldehyde, nine related low-molecular-weight-aldehydes.
However, the limited studies to date indicate that these substances have
chemical reactivity and mutagenicity similar to acetaldehyde and
malonaldehyde. Therefore, NIOSH recommends that careful consideration should
be given to reducing exposures
to these nine related aldehydes.
Further information can be found in the "NIOSH
Current Intelligence Bulletin 55: Carcinogenicity of Acetaldehyde and
Malonaldehyde, and Mutagenicity of Related Low-Molecular-Weight Aldehydes"
[DHHS (NIOSH) Publication No. 91-112.]
Asbestos
NIOSH considers asbestos to be a potential occupational carcinogen and recommends that exposures be reduced to the lowest feasible concentration. For asbestos fibers >5 micrometers in length, NIOSH recommends a REL of 100,000 fibers per cubic meter of air (100,000 fibers/m3), which is equal to 0.1 fiber per cubic centimeter of air (0.1 fiber/cm3), as determined by a 400-liter air sample collected over 100 minutes in accordance with NIOSH Analytical Method #7400. Airborne asbestos fibers are defined as those particles having (1) an aspect ratio of 3 to 1 or greater and (2) the mineralogic characteristics (that is, the crystal structure and elemental composition) of the asbestos minerals and their nonasbestiform analogs. The asbestos minerals are defined as chrysotile, crocidolite, amosite (cummingtonite-grunerite), anthophyllite, tremolite, and actinolite. In addition, airborne cleavage fragments from the nonasbestiform habits of the serpentine minerals antigorite and lizardite, and the amphibole minerals contained in the series cummingtonite-grunerite, tremolite-ferroactinolite, and glaucophane-riebeckite should also be counted as fibers provided they meet the criteria for a fiber when viewed microscopically.
As found in 29 CFR 1910.1001, the OSHA PEL for asbestos fibers (i.e.,
actinolite asbestos, amosite, anthophyllite asbestos, chrysotile, crocidolite,
and tremolite asbestos) is an 8-hour TWA airborne concentration of 0.1 fiber
(longer than 5 micrometers and having a length-to-diameter ratio of at least 3
to 1)
per cubic centimeter of air (0.1 fiber/cm3), as determined by the
membrane filter method at approximately 400X magnification with phase contrast
illumination. No worker should be exposed in excess of 1 fiber/cm3
(excursion limit)as averaged over a sampling period of 30 minutes.
Benzidine-, o-Tolidine, and o-Dianisidine-based Dyes
In December 1980, OSHA and NIOSH jointly published the Health Hazard
Alert: Benzidine-, o-Tolidine-, and o-Dianisidine-based Dyes.
In this Alert, OSHA and NIOSH concluded that benzidine and benzidine-based
dyes were potential occupational carcinogens and recommended that worker
exposure be reduced to the lowest feasible level.
OSHA and NIOSH further concluded that o-tolidine and o-dianisidine (and
dyes based on them) may present a cancer risk to workers and should be
handled with caution and exposure minimized.
Carbon Black
NIOSH considers "Carbon Black" to be the material consisting of more
than 80% elemental carbon in the form of near-spherical colloidal particles
and
coalesced particle aggregates of colloidal size that is obtained by the
partial
combustion or thermal decomposition of hydrocarbons.
The NIOSH REL (10-hour TWA) for carbon black is 3.5 mg/m3.
Polycyclic aromatic hydrocarbons (PAHs), particulate polycyclic organic
material (PPOM), and polynuclear aromatic hydrocarbons (PNAs) are terms
frequently used to describe various petroleum-based substances that NIOSH
considers to be potential occupational carcinogens.
Since some of these aromatic hydrocarbons may be formed during the
manufacture of carbon black (and become adsorbed on the carbon black), the
NIOSH REL
(10-hour TWA) for carbon black in the presence of PAHs is also 0.1 mg
PAHs/m3 (measured as the cyclohexane-extractable fraction).
The OSHA PEL (8-hour TWA) for carbon black is 3.5 mg/m3.
Chloroethanes
NIOSH considers ethylene dichloride; hexachloroethane;
1,1,2,2-tetrachloroethane; and 1,1,2-trichloroethane; to be potential
occupational carcinogens.
Additionally, NIOSH recommends that the other five chloroethane
compounds:
1,1-dichloroethane
ethyl chloride
methyl chloroform
pentachloroethane
1,1,1,2-tetrachloroethane
be treated in the workplace with caution because of their structural
similarity to the four chloroethanes shown to be carcinogenic in animals.
Chromic Acid and Chromates (as CrO3), Chromium(II) and
Chromium(III) Compounds (as Cr), and Chromium Metal (as Cr)
The NIOSH REL (10-hour TWA) is 0.001 mg Cr(VI)/m3 for all
hexavalent chromium [Cr(VI)] compounds. NIOSH considers all Cr(VI) compounds
(including chromic acid, tert-butyl chromate, zinc chromate, and chromyl
chloride) to be potential occupational carcinogens.
The NIOSH REL (8-hour TWA) is 0.5 mg Cr/m3 for chromium
metal and chromium(II) and chromium(III) compounds.
The OSHA PEL is 0.1 mg CrO3/m3 (ceiling) for
chromic acid and chromates (including tert-butyl chromate with a "skin"
designation and zinc chromate); 0.5 mg Cr/m3 (8-hour TWA) for
chromium(II) and chromium(III)
compounds; and 1 mg Cr/m3 (8-hour TWA) for chromium metal and
insoluble salts.
Coal Tar Pitch Volatiles
NIOSH considers coal tar products (i.e., coal tar, coal tar pitch, or
creosote) to be potential occupational carcinogens; the NIOSH REL (10-hour
TWA) for coal tar products is 0.1 mg/m3 (cyclohexane-extractable
fraction).
The OSHA PEL (8-hour TWA) for coal tar pitch volatiles is 0.2
mg/m3 (benzene-soluble fraction). OSHA defines "coal tar pitch
volatiles" in 29 CFR 1910.1002 as the fused polycyclic hydrocarbons that
volatilize from the
distillation residues of coal, petroleum (excluding asphalt), wood, and other
organic matter and includes substances such as anthracene, benzo(a)pyrene
(BaP), phenanthrene, acridine, chrysene, pyrene, etc.
Coke Oven Emissions
The production of coke by the carbonization of bituminous coal leads to the
release of chemically-complex emissions from coke ovens that include both
gases and
particulate matter of varying chemical composition.
The emissions include coal tar
pitch volatiles (e.g., particulate polycyclic organic matter [PPOM],
polycyclic aromatic hydrocarbons [PAHs], and polynuclear aromatic hydrocarbons
[PNAs]),
aromatic compounds (e.g., benzene and beta-naphthylamine), trace metals (e.g.,
arsenic, beryllium, cadmium, chromium, lead, and nickel), and gases (e.g.,
nitric
oxides and sulfur dioxide).
Cotton Dust (raw)
NIOSH recommends reducing exposures to cotton dust to the lowest
feasible concentration to reduce the prevalence and severity of byssinosis;
the REL is
<0.200 mg/m3 (as lint-free cotton dust).
As found in OSHA Table Z-1 (29 CFR 1910.1000), the PEL for cotton dust
(raw) is 1 mg/m3 for the cotton waste processing operations of
waste
recycling (sorting, blending, cleaning, and willowing) and garnetting.
PELs for other sectors (as found in 29 CFR 1910.1043) are 0.200
mg/m3 for yarn manufacturing and cotton washing operations, 0.500
mg/m3 for textile mill waste house operations or for dust from
"lower grade washed cotton" used during yarn manufacturing, and 0.750
mg/m3 for textile slashing and weaving operations.
The OSHA standard in 29 CFR 1910.1043 does not apply to cotton harvesting,
ginning, or the handling and processing of woven or knitted materials and
washed cotton.
All PELs for cotton dust are mean concentrations of lint-free, respirable
cotton dust collected by the vertical elutriator or an equivalent method and
averaged over an 8-hour period.
Lead
NIOSH considers "Lead" to mean metallic lead, lead oxides, and lead
salts (including organic salts such as lead soaps but excluding lead
arsenate).
The NIOSH REL for lead (8-hour TWA) is 0.050 mg/m3; air
concentrations should be maintained so that worker blood lead remains less
than 0.060 mg Pb/100 g of whole blood.
OSHA considers "Lead" to mean metallic lead, all inorganic lead
compounds (lead oxides and lead salts), and a class of organic compounds
called soaps;
all other lead compounds are excluded from this definition.
The OSHA PEL (8-hour TWA) is 0.050 mg/m3; other OSHA requirements
can be found in 29 CFR 1910.1025. The OSHA PEL (8-hour TWA) for lead in
"non-ferrous foundries with less than 20 employees" is 0.075 mg/m3.
Mineral Dusts
These OSHA PELs for "mineral dusts" listed below are from Table Z-3 of
29 CFR 1910.1000.
The OSHA PEL (8-hour TWA) for crystalline silica (as respirable
quartz) is either 250 mppcf divided by the value "%SiO2 + 5" or
10 mg/m3 divided by the value "%SiO2 + 2".
The OSHA PEL (8-hour TWA) for crystalline silica (as total quartz) is 30
mg/m3 divided by the value "%SiO2 + 2".
The OSHA PELs (8-hour TWAs) for cristobalite and tridymite are the values
calculated above using the count or mass formulae for quartz.
The OSHA PEL (8-hour TWA) for amorphous silica (including diatomaceous
earth) is either 80 mg/m3 divided by the value "%SiO2",
or 20
mppcf.
The OSHA PELs (8-hour TWAs) for mica, soapstone, and talc (not
containing asbestos) are 20 mppcf.
The OSHA PEL (8-hour TWA) for Portland cement is 50 mppcf.
The OSHA PEL (8-hour TWA) for graphite (natural) is 15 mppcf.
The OSHA PEL (8-hour TWA) for coal dust (as the respirable fraction)
containing less than 5% SiO2 is 2.4 mg/m3.
The OSHA PEL (8-hour TWA) for coal dust (as the respirable fraction)
containing greater than 5% SiO2 is 10 mg/m3 divided by
the value
"%SiO2 + 2".
NIAX® Catalyst ESN
In May 1978, OSHA and NIOSH jointly published the Current Intelligence
Bulletin (CIB) 26: NIAX® Catalyst ESN.
In this CIB, OSHA and NIOSH recommended that occupational exposure to
NIAX® Catalyst ESN, its components, dimethylaminopropionitrile and
bis(2-(dimethylamino)ethyl)ether, as well as formulations containing either
component, be minimized.
Exposures should be limited to as few workers as possible, while minimizing
workplace exposure concentrations with effective work practices and
engineering controls.
Exposed workers should be carefully monitored for potential disorders of the
nervous and genitourinary system. Although substitution is a possible control
measure,
alternatives to NIAX® Catalyst ESN or its components should be carefully
evaluated with regard to possible adverse health effects.
Trichloroethylene
NIOSH considers trichloroethylene (TCE) to be a potential occupational
carcinogen and recommends a REL of 2 ppm (as a 60-minute ceiling) during
the usage of TCE as an anesthetic agent and 25 ppm (as a 10-hour TWA) during
all other
exposures.
Tungsten Carbide (Cemented)
"Cemented tungsten carbide" or "hard metal" refers to a mixture of tungsten
carbide, cobalt, and sometimes metal oxides or carbides and other metals
(including nickel).
When the cobalt (Co) content exceeds 2%, its contribution to the
potential hazard is judged to exceed that of tungsten carbide.
Therefore, the NIOSH REL (10-hour TWA) for cemented tungsten carbide
containing >2% Co is 0.05 mg Co/m3; the applicable OSHA PEL is 0.1
mg
Co/m3 (8-hour TWA). Nickel (Ni) may sometimes be used as a binder
rather than cobalt.
NIOSH considers cemented tungsten carbide containing nickel to be a potential
occupational carcinogen and recommends a REL of 0.015 mg Ni/m3
(10-hour TWA).
The OSHA PEL for Insoluble Nickel (i.e., a 1 mg Ni/m3 8-hour TWA)
applies to mixtures of tungsten carbide and nickel.
APPENDIX D
SUBSTANCES WITH NO ESTABLISHED RELs
After reviewing available published literature, NIOSH provided comments
to OSHA on August 1, 1988, regarding the "Proposed Rule on Air Contaminants"
(29 CFR 1910, Docket No. H-020).
In these comments, NIOSH questioned whether the PELs proposed (and listed
below) for the following substances included in the Pocket Guide were adequate
to protect workers from recognized health hazards:
acetylene tetrabromide [TWA 1 ppm]
chlorobenzene [TWA 75 ppm]
coal dust (<5%SiO2) [2 mg/m3 (as the respirable
dust fraction)], coal dust (>/= 5% SiO2) [0.1
mg/m3
(as the respirable quartz fraction)]
ethyl bromide [TWA 200 ppm; STEL 250 ppm]
ethylene glycol [Ceiling 50 ppm]
ethyl ether [TWA 400 ppm; STEL 500 ppm]
fenthion [TWA 0.2 mg/m3 (skin)]
furfural [TWA 2 ppm (skin)]
2-isopropoxyethanol [TWA 25 ppm]
isopropyl acetate [TWA 250 ppm; STEL 310 ppm]
isopropylamine [TWA 5 ppm; STEL 10 ppm]
manganese tetroxide (as Mn) [TWA 1 mg/m3]
molybdenum (soluble compounds as Mo) [TWA 5 mg/m3]
nitromethane [TWA 100 ppm]
m-toluidine [TWA 2 ppm (skin)]
triethylamine [TWA 10 ppm; STEL 15 ppm]
At that time, NIOSH also conducted a limited evaluation of the
literature and concluded that the documentation cited by OSHA was inadequate
to support
the proposed PEL (as an 8-hour TWA) of 10 mg/m3 for alpha-alumina,
benomyl, emery, glycerine (mist), graphite (synthetic), magnesium oxide fume,
molybdenum (insoluble compounds as Mo), particulates not otherwise regulated,
picloram, and rouge.
APPENDIX E
RESPIRATOR RECOMMENDATIONS FOR SELECTED CHEMICALS
Mercury compounds [except (organo) alkyls]
NIOSH
Up to 0.5 mg/m3: | (APF = 10) Any chemical cartridge respirator with cartridge(s) providing protection against the compound of concern/ (APF = 10) Any supplied air respirator |
Up to 1.25 mg/m3: | (APF = 25) Any supplied-air respirator operated in a continuous-flow mode/ (APF = 25) Any powered, air-purifying respirator with cartridge(s) providing protection against the compound of concern |
Up to 2.5 mg/m3: | (APF = 50) Any chemical cartridge respirator with a full facepiece and cartridge(s) providing protection against the compound of concern/ (APF = 50) Any air-purifying, full-facepiece respirator (gas mask) with a chin-style, front- or back-mounted canister providing protection against the compound of concern/ (APF = 50) Any supplied-air respirator that has a tight-fitting facepiece and is operated in a continuous-flow mode/ (APF = 50) Any powered, air-purifying respirator with a tight-fitting facepiece and cartridge(s) providing protection against the compound of concern/ (APF = 50) Any self-contained breathing apparatus that has a full facepiece/ (APF = 50) Any supplied-air respirator with a full facepiece |
Up to 10 mg/m3: | (APF = 1000) Any supplied-air respirator operated in a pressure-demand or other positive-pressure mode |
Emergency or planned entry into unknown concentrations or IDLH conditions: | (APF = 10,000) Any self-contained breathing apparatus that has a full facepiece and is operated in a pressure-demand or other positive-pressure mode/ (APF = 10,000) Any supplied-air respirator that has a full facepiece and is operated in a pressure-demand or other positive-pressure mode in combination with an auxiliary self-contained breathing apparatus operated in pressure-demand or other positive-pressure mode |
Escape: | (APF = 50) Any air-purifying, full-facepiece respirator (gas mask) with a chin-style, front- or back-mounted canister providing protection against the compund of concern/ Any appropriate escape-type, self-contained breathing apparatus |
NIOSH/OSHA
Up to 1 mg/m3: | (APF = 10) Any chemical cartridge respirator with cartridge(s) providing protection against the compound of concern/ (APF = 10) Any supplied air respirator |
Up to 2.5 mg/m3: | (APF = 25) Any supplied-air respirator operated in a continuous-flow mode/ (APF = 25) Any powered, air-purifying respirator with cartridge(s) providing protection against the compound of concern |
Up to 5 mg/m3: | (APF = 50) Any chemical cartridge respirator with a full facepiece and cartridge(s) providing protection against the compound of concern/ (APF = 50) Any air-purifying, full-facepiece respirator (gas mask) with a chin-style, front- or back-mounted canister providing protection against the compound of concern/ (APF = 50) Any supplied-air respirator that has a tight-fitting facepiece and is operated in a continuous-flow mode/ (APF = 50) Any powered, air-purifying respirator with a tight-fitting facepiece and cartridge(s) providing protection against the compound of concern/ (APF = 50) Any self-contained breathing apparatus that has a full facepiece/ (APF = 50) Any supplied-air respirator with a full facepiece |
Up to 10 mg/m3: | (APF = 1000) Any supplied-air respirator operated in a pressure-demand or other positive-pressure mode |
Emergency or planned entry into unknown concentrations or IDLH conditions: | (APF = 10,000) Any self-contained breathing apparatus that has a full facepiece and is operated in a pressure-demand or other positive-pressure mode/ (APF = 10,000) Any supplied-air respirator that has a full facepiece and is operated in a pressure-demand or other positive-pressure mode in combination with an auxiliary self-contained breathing apparatus operated in pressure-demand or other positive-pressure mode |
Escape: | (APF = 50) Any air-purifying, full-facepiece respirator (gas mask) with a chin-style, front- or back-mounted canister providing protection against the compund of concern/ Any appropriate escape-type, self-contained breathing apparatus |
MISCELLANEOUS
NOTES
Benzene: The final OSHA Benzene standard in 1910.1028 applies to all
occupational exposures to benzene except some subsegments of industry where
exposures are consistently under the action level (i.e., distribution and
sales
of fuels, sealed containers and pipelines, coke production, oil and gas
drilling
and production, natural gas processing, and the percentage exclusion for
liquid mixtures); for the excepted subsegments, the benzene limits in Table
Z-2
apply (i.e., an 8-hour TWA of 10 ppm, an acceptable ceiling of 25 ppm, and
50 ppm for a maximum duration of 10 minutes as an acceptable maximum peak
above the acceptable ceiling).
APPENDIX G
1989 AIR CONTAMINANTS UPDATE PROJECT:
EXPOSURE LIMITS NOT IN EFFECT
Acetaldehyde | TWA 100 ppm (180 mg/m3) ST 150 ppm (270 mg/m3) |
Acetic anhydride | C 5 ppm (20 mg/m3) |
Acetone | TWA 750 ppm (1800 mg/m3) ST 1000 ppm (2400 mg/m3) |
Acetonitrile | TWA 40 ppm (70 mg/m3) ST 60 ppm (105 mg/m3) |
Acetylsalicyclic acid | TWA 5 mg/m3 |
Acrolein | TWA 0.1 ppm (0.25 mg/m3) ST 0.3 ppm (0.8 mg/m3) |
Acrylamide | TWA 0.03 mg/m3 [skin] |
Acrylic acid | TWA 10 ppm (30 mg/m3) [skin] |
Allyl alcohol | TWA 2 ppm (5 mg/m3) ST 4 ppm (10 mg/m3) [skin] |
Allyl chloride | TWA 1 ppm (3 mg/m3) ST 2 ppm (6 mg/m3) |
Allyl glycidyl ether | TWA 5 ppm (22 mg/m3) ST 10 ppm (44 mg/m3) |
Allyl propyl disulfide | TWA 2 ppm (12 mg/m3) ST 3 ppm (18 mg/m3) |
alpha-Alumina | TWA 10 mg/m3 (total) TWA 5 mg/m3 (resp) |
Aluminum (pyro powders & welding fumes, as Al) | TWA 5 mg/m3 |
Aluminum (soluble salts & alkyls, as Al) | TWA 2 mg/m3 |
Amitrole | TWA 0.2 mg/m3 |
Ammonia | ST 35 ppm (27 mg/m3) |
Ammonium chloride fume | TWA 10 mg/m3 ST 20 mg/m3 |
Ammonium sulfamate | TWA 10 mg/m3 (total) TWA 5 mg/m3 (resp) |
Aniline (and homologs) | TWA 2 ppm (8 mg/m3) [skin] |
Atrazine | TWA 5 mg/m3 |
Barium sulfate | TWA 10 mg/m3 (total) TWA 5 mg/m3 (resp) |
Benomyl | TWA 10 mg/m3 (total) TWA 5 mg/m3 (resp) |
Benzenethiol | TWA 0.5 ppm (2 mg/m3) |
Bismuth telluride (doped with selenium sulfide, as Bi2Te3) | TWA 5 mg/m3 |
Borates, tetra, sodium salts (Anhydrous) | TWA 10 mg/m3 |
Borates, tetra, sodium salts (Decahydrate) | TWA 10 mg/m3 |
Borates, tetra, sodium salts (Pentahydrate) | TWA 10 mg/m3 |
Boron oxide | TWA 10 mg/m3 |
Boron tribromide | C 1 ppm (10 mg/m3) |
Bromacil | TWA 1 ppm (10 mg/m3) |
Bromine | TWA 0.1 ppm (0.7 mg/m3) ST 0.3 ppm (2 mg/m3) |
Bromine pentafluoride | TWA 0.1 ppm (0.7 mg/m3) |
n-Butane | TWA 800 ppm (1900 mg/m3) |
2-Butanone | TWA 200 ppm (590 mg/m3) ST 300 ppm (885 mg/m3) |
2-Butoxyethanol | TWA 25 ppm (120 mg/m3) [skin] |
n-Butyl acetate | TWA 150 ppm (710 mg/m3) ST 200 ppm (950 mg/m3) |
Butyl acrylate | TWA 10 ppm (55 mg/m3) |
n-Butyl alcohol | C 50 ppm (150 mg/m3) [skin] |
sec-Butyl alcohol | TWA 100 ppm (305 mg/m3) |
tert-Butyl alcohol | TWA 100 ppm (300 mg/m3) ST 150 ppm (450 mg/m3) |
n-Butyl glycidyl ether | TWA 25 ppm (135 mg/m3) |
n-Butyl lactate | TWA 5 ppm (25 mg/m3) |
n-Butyl mercaptan | TWA 0.5 ppm (1.5 mg/m3) |
o-sec-Butylphenol | TWA 5 ppm (30 mg/m3) [skin] |
p-tert-Butyltoluene | TWA 10 ppm (60 mg/m3) ST 20 ppm (120 mg/m3) |
Calcium cyanamide | TWA 0.5 mg/m3 |
Caprolactam | Dust: TWA 1 mg/m3 ST 3 mg/m3 Vapor: TWA 5 ppm (20 mg/m3) ST 10 ppm (40 mg/m3) |
Captafol | TWA 0.1 mg/m3 |
Captan | TWA 5 mg/m3 |
Carbofuran | TWA 0.1 mg/m3 |
Carbon dioxide | TWA 10,000 ppm (18,000 mg/m3) ST 30,000 ppm (54,000 mg/m3) |
Carbon disulfide | TWA 4 ppm (12 mg/m3) ST 12 ppm (36 mg/m3) [skin] |
Carbon monoxide | TWA 35 ppm (40 mg/m3) C 200 ppm (229 mg/m3) |
Carbon tetrabromide | TWA 0.1 ppm (1.4 mg/m3) ST 0.3 ppm (4 mg/m3) |
Carbon tetrachloride | TWA 2 ppm (12.6 mg/m3) |
Carbonyl fluoride | TWA 2 ppm (5 mg/m3) ST 5 ppm (15 mg/m3) |
Catechol | TWA 5 ppm (20 mg/m3) [skin] |
Cesium hydroxide | TWA 2 mg/m3 |
Chlorinated camphene | TWA 0.5 mg/m3 ST 1 mg/m3 [skin] |
Chlorine | TWA 0.5 ppm (1.5 mg/m3) ST 1 ppm (3 mg/m3) |
Chlorine dioxide | TWA 0.1 ppm (0.3 mg/m3) ST 0.3 ppm (0.9 mg/m3) |
Chloroacetyl chloride | TWA 0.05 ppm (0.2 mg/m3) |
o-Chlorobenzylidene malononitrile | C 0.05 ppm (0.4 mg/m3) [skin] |
Chlorodifluoromethane | TWA 1000 ppm (3500 mg/m3) |
Chloroform | TWA 2 ppm (9.78 mg/m3) |
1-Chloro-1-nitropropane | TWA 2 ppm (10 mg/m3) |
Chloropentafluoroethane | TWA 1000 ppm (6320 mg/m3) |
beta-Chloroprene | TWA 10 ppm (35 mg/m3) [skin] |
o-Chlorostyrene | TWA 50 ppm (285 mg/m3) ST 75 ppm (428 mg/m3) |
o-Chlorotoluene | TWA 50 ppm (250 mg/m3) |
Chlorpyrifos | TWA 0.2 mg/m3 [skin] |
Coal dust | TWA 2 mg/m3 (<5%
SiO2)(resp dust) TWA 0.1 mg/m3 (>/= 5% SiO2) (resp quartz) |
Cobalt metal dust & fume, as Co) | TWA 0.05 mg/m3 |
Cobalt carbonyl (as Co) | TWA 0.1 mg/m3 |
Cobalt hydrocarbonyl (as Co) | TWA 0.1 mg/m3 |
Crag® herbicide | TWA 10 mg/m3 (total) TWA 5 mg/m3 (resp) |
Crufomate | TWA 5 mg/m3 |
Cyanamide | TWA 2 mg/m3 |
Cyanogen | TWA 10 ppm (20 mg/m3) |
Cyanogen chloride | C 0.3 ppm (0.6 mg/m3) |
Cyclohexanol | TWA 50 ppm (200 mg/m3) [skin] |
Cyclohexanone | TWA 25 ppm (100 mg/m3) [skin] |
Cyclohexylamine | TWA 10 ppm (40 mg/m3) |
Cyclonite | TWA 1.5 mg/m3 [skin] |
Cyclopentane | TWA 600 ppm (1720 mg/m3) |
Cyhexatin | TWA 5 mg/m3 |
Decaborane | TWA 0.3 mg/m3 (0.05 ppm) ST 0.9 mg/m3 (0.15 ppm) [skin] |
Diazinon | TWA 0.1 mg/m3 [skin] |
2-N-Dibutylaminoethanol | TWA 2 ppm (14 mg/m3) |
Dibutyl phosphate | TWA 1 ppm (5 mg/m3) ST 2 ppm (10 mg/m3) |
Dichloroacetylene | C 0.1 ppm (0.4 mg/m3) |
p-Dichlorobenzene | TWA 75 ppm (450 mg/m3) ST 110 ppm (675 mg/m3) |
1,3-Dichloro-5,5-dimethylhydantoin | TWA 0.2 mg/m3 ST 0.4 mg/m3 |
Dichloroethyl ether | TWA 5 ppm (30 mg/m3) ST 10 ppm (60 mg/m3) [skin] |
Dichloromonofluoromethane | TWA 10 ppm (40 mg/m3) |
1,1-Dichloro-1-nitroethane | TWA 2 ppm (10 mg/m3) |
1,3-Dichloropropene | TWA 1 ppm (5 mg/m3) [skin] |
2,2-Dichloropropionic acid | TWA 1 ppm (6 mg/m3) |
Dicrotophos | TWA 0.25 mg/m3 [skin] |
Dicyclopentadiene | TWA 5 ppm (30 mg/m3) |
Dicyclopentadienyl iron | TWA 10 mg/m3 (total) TWA 5 mg/m3 (resp) |
Diethanolamine | TWA 3 ppm (15 mg/m3) |
Diethylamine | TWA 10 ppm (30 mg/m3) ST 25 ppm (75 mg/m3) |
Diethylenetriamine | TWA 1 ppm (4 mg/m3) |
Diethyl ketone | TWA 200 ppm (705 mg/m3) |
Diethyl phthalate | TWA 5 mg/m3 |
Diglycidyl ether | TWA 0.1 ppm (0.5 mg/m3) |
Diisobutyl ketone | TWA 25 ppm (150 mg/m3) |
N,N-Dimethylaniline | TWA 5 ppm (25 mg/m3) ST 10 ppm (50 mg/m3) [skin] |
Dimethyl-1,2-dibromo-2,2-dichlorethyl phosphate | TWA 3 mg/m3 [skin] |
Dimethyl sulfate | TWA 0.1 ppm (0.5 mg/m3) [skin] |
Dinitolmide | TWA 5 mg/m3 |
Di-sec octyl phthalate | TWA 5 mg/m3 ST 10 mg/m3 |
Dioxane | TWA 25 ppm (90 mg/m3) [skin] |
Dioxathion | TWA 0.2 mg/m3 [skin] |
Diphenylamine | TWA 10 mg/m3 |
Dipropylene glycol methyl ether | TWA 100 ppm (600 mg/m3) ST 150 ppm (900 mg/m3) [skin] |
Dipropyl ketone | TWA 50 ppm (235 mg/m3) |
Diquat (Diquat dibromide) | TWA 0.5 mg/m3 |
Disulfiram | TWA 2 mg/m3 |
Disulfoton | TWA 0.1 mg/m3 [skin] |
2,6-Di-tert-butyl-p-cresol | TWA 10 mg/m3 |
Diuron | TWA 10 mg/m3 |
Divinyl benzene | TWA 10 ppm (50 mg/m3) |
Emery | TWA 10 mg/m3 (total) TWA 5 mg/m3 (resp) |
Endosulfan | TWA 0.1 mg/m3 [skin] |
Epichlorohydrin | TWA 2 ppm (8 mg/m3) [skin] |
Ethanolamine | TWA 3 ppm (8 mg/m3) ST 6 ppm (15 mg/m3) |
Ethion | 0.4 mg/m3 [skin] |
Ethyl acrylate | TWA 5 ppm (20 mg/m3) ST 25 ppm (100 mg/m3) [skin] |
Ethyl benzene | TWA 100 ppm (435 mg/m3) ST 125 ppm (545 mg/m3) |
Ethyl bromide | TWA 200 ppm (890 mg/m3) ST 250 ppm (1110 mg/m3) |
Ethylene chlorohydrin | C 1 ppm (3 mg/m3) [skin] |
Ethylene dichloride | TWA 1 ppm (4 mg/m3) ST 2 ppm (8 mg/m3) |
Ethylene glycol | C 50 ppm (125 mg/m3) |
Ethylene glycol dinitrate | ST 0.1 mg/m3 [skin] |
Ethyl ether | TWA 400 ppm (1200 mg/m3) ST 500 ppm (1500 mg/m3) |
Ethylidene norbornene | C 5 ppm (25 mg/m3) |
Ethyl mercaptan | TWA 0.5 ppm (1 mg/m3) |
N-Ethylmorpholine | TWA 5 ppm (23 mg/m3) [skin] |
Ethyl silicate | TWA 10 ppm (85 mg/m3) |
Fenamiphos | TWA 0.1 mg/m3 [skin] |
Fensulfothion | TWA 0.1 mg/m3 |
Fenthion | TWA 0.2 mg/m3 [skin] |
Ferbam | TWA 10 mg/m3 |
Ferrovanadium dust | TWA 1 mg/m3 ST 3 mg/m3 |
Fluorotrichloromethane | C 1000 ppm (5600 mg/m3) |
Fonofos | TWA 0.1 mg/m3 [skin] |
Formamide | TWA 20 ppm (30 mg/m3) ST 30 ppm (45 mg/m3) |
Furfural | TWA 2 ppm (8 mg/m3) [skin] |
Furfuryl alcohol | TWA 10 ppm (40 mg/m3) ST 15 ppm (60 mg/m3) [skin] |
Gasoline | TWA 300 ppm (900 mg/m3) ST 500 ppm (1500 mg/m3) |
Germanium tetrahydride | TWA 0.2 ppm (0.6 mg/m3) |
Glutaraldehyde | C 0.2 ppm (0.8 mg/m3) |
Glycerin (mist) | TWA 10 mg/m3 (total) TWA 5 mg/m3 (resp) |
Glycidol | TWA 25 ppm (75 mg/m3) |
Graphite (natural) | TWA 2.5 mg/m3 (resp) |
Graphite (synthetic) | TWA 10 mg/m3 (total) TWA 5 mg/m3 (resp) |
n-Heptane | TWA 400 ppm (1600 mg/m3) ST 500 ppm (2000 mg/m3) |
Hexachlorobutadiene | TWA 0.02 ppm (0.24 mg/m3) |
Hexachlorocyclopentadiene | TWA 0.01 ppm (0.1 mg/m3) |
Hexafluoroacetone | TWA 0.1 ppm (0.7 mg/m3) [skin] |
n-Hexane | TWA 50 ppm (180 mg/m3) |
Hexane isomers (except n-Hexane) | TWA 500 ppm (1800 mg/m3) ST 1000 ppm (3600 mg/m3) |
2-Hexanone | TWA 5 ppm (20 mg/m3) |
Hexone | TWA 50 ppm (205 mg/m3) ST 75 ppm (300 mg/m3) |
Hexylene glycol | C 25 ppm (125 mg/m3) |
Hydrazine | TWA 0.1 ppm (0.1 mg/m3) [skin] |
Hydrogenated terphenyls | TWA 0.5 ppm (5 mg/m3) |
Hydrogen bromide | C 3 ppm (10 mg/m3) |
Hydrogen cyanide | ST 4.7 ppm (5 mg/m3) [skin] |
Hydrogen fluoride (as F) | TWA 3 ppm ST 6 ppm |
Hydrogen sulfide | TWA 10 ppm (14 mg/m3) ST 15 ppm (21 mg/m3) |
2-Hydroxypropyl acrylate | TWA 0.5 ppm (3 mg/m3) [skin] |
Indene | TWA 10 ppm (45 mg/m3) |
Indium | TWA 0.1 mg/m3 |
Iodoform | TWA 0.6 ppm (10 mg/m3) |
Iron pentacarbonyl (as Fe) | TWA 0.1 ppm (0.8 mg/m3) ST 0.2 ppm (1.6 mg/m3) |
Iron salts (soluble, as Fe) | TWA 1 mg/m3 |
Isoamyl alcohol (primary & secondary) | TWA 100 ppm (360 mg/m3) ST 125 ppm (450 mg/m3) |
Isobutane | TWA 800 ppm (1900 mg/m3) |
Isobutyl alcohol | TWA 50 ppm (150 mg/m3) |
Isooctyl alcohol | TWA 50 ppm (270 mg/m3) [skin] |
Isophorone | TWA 4 ppm (23 mg/m3) |
Isophorone diisocyanate | TWA 0.005 ppm ST 0.02 ppm [skin] |
2-Isopropoxyethanol | TWA 25 ppm (105 mg/m3) |
Isopropyl acetate | TWA 250 ppm (950 mg/m3) ST 310 ppm (1185 mg/m3) |
Isopropyl alcohol | TWA 400 ppm (980 mg/m3) ST 500 ppm (1225 mg/m3) |
Isopropylamine | TWA 5 ppm (12 mg/m3) ST 10 ppm (24 mg/m3) |
N-Isopropylaniline | TWA 2 ppm (10 mg/m3) [skin] |
Isopropyl glycidyl ether | TWA 50 ppm (240 mg/m3) ST 75 ppm (360 mg/m3) |
Kaolin | TWA 10 mg/m3 (total) TWA 5 mg/m3 (resp) |
Ketene | TWA 0.5 ppm (0.9 mg/m3) ST 1.5 ppm (3 mg/m3) |
Magnesium oxide fume | TWA 10 mg/m3 |
Malathion | TWA 10 mg/m3 [skin] |
Manganese compounds and fume (as Mn) | Compounds: C 5 mg/m3 Fume: TWA 1 mg/m3 ST 3 mg/m3 |
Manganese cyclopentadienyl tricarbonyl (as Mn) | TWA 0.1 mg/m3 [skin] |
Manganese tetroxide (as Mn) | TWA 1 mg/m3 |
Mercury compounds, as Hg [except(organo) alkyls] | |
TWA 0.05 mg/m3 [skin] | |
C 0.1 mg/m3 [skin] | |
Mercury (organo) alkyl compounds (as Hg) | TWA 0.01 mg/m3 ST 0.03 mg/m3 [skin] |
Mesityl oxide | TWA 15 ppm (60 mg/m3) ST 25 ppm (100 mg/m3) |
Methacrylic acid | TWA 20 ppm (70 mg/m3) [skin] |
Methomyl | TWA 2.5 mg/m3 |
Methoxychlor | TWA 10 mg/m3 |
4-Methoxyphenol | TWA 5 mg/m3 |
Methyl acetate | TWA 200 ppm (610 mg/m3) ST 250 ppm (760 mg/m3) |
Methyl acetylene-propadiene mixture | TWA 1000 ppm (1800 mg/m3) ST 1250 ppm (2250 mg/m3) |
Methylacrylonitrile | TWA 1 ppm (3 mg/m3) [skin] |
Methyl alcohol | TWA 200 ppm (260 mg/m3) ST 250 ppm (325 mg/m3) [skin] |
Methyl bromide | TWA 5 ppm (20 mg/m3) [skin] |
Methyl chloride | TWA 50 ppm (105 mg/m3) ST 100 ppm (210 mg/m3) |
Methyl chloroform | TWA 350 ppm (1900 mg/m3) ST 450 ppm (2450 mg/m3) |
Methyl-2-cyanoacrylate | TWA 2 ppm (8 mg/m3) ST 4 ppm (16 mg/m3) |
Methylcyclohexane | TWA 400 ppm (1600 mg/m3) |
Methylcyclohexanol | TWA 50 ppm (235 mg/m3) |
o-Methylcyclohexanone | TWA 50 ppm (230 mg/m3) ST 75 ppm (345 mg/m3) [skin] |
Methyl cyclopentadienyl manganese tricarbonyl (as Mn) | TWA 0.2 mg/m3 [skin] |
Methyl demeton | TWA 0.5 mg/m3 [skin] |
4,4'-Methylenebis(2-chloroaniline) | TWA 0.02 ppm (0.22 mg/m3) [skin] |
Methylene bis(4-cyclo-hexylisocyanate) | C 0.01 ppm (0.11 mg/m3) [skin] |
Methyl ethyl ketone peroxide | C 0.7 ppm (5 mg/m3) |
Methyl formate | TWA 100 ppm (250 mg/m3) ST 150 ppm (375 mg/m3) |
Methyl iodide | TWA 2 ppm (10 mg/m3) [skin] |
Methyl isoamyl ketone | TWA 50 ppm (240 mg/m3) |
Methyl isobutyl carbinol | TWA 25 ppm (100 mg/m3) ST 40 ppm (165 mg/m3) [skin] |
Methyl isopropyl ketone | TWA 200 ppm (705 mg/m3) |
Methyl mercaptan | TWA 0.5 ppm (1 mg/m3) |
Methyl parathion | TWA 0.2 mg/m3 [skin] |
Methyl silicate | TWA 1 ppm (6 mg/m3) |
alpha-Methyl styrene | TWA 50 ppm (240 mg/m3) ST 100 ppm (485 mg/m3) |
Metribuzin | TWA 5 mg/m3 |
Mica | TWA 3 mg/m3 (resp) |
Molybdenum (insoluble compounds, as Mo) | TWA 10 mg/m3 |
Monocrotophos | TWA 0.25 mg/m3 |
Monomethyl aniline | TWA 0.5 ppm (2 mg/m3) [skin] |
Morpholine | TWA 20 ppm (70 mg/m3) ST 30 ppm (105 mg/m3) [skin] |
Naphthalene | TWA 10 ppm (50 mg/m3) ST 15 ppm (75 mg/m3) |
Nickel metal & other compounds (as Ni) | |
TWA 1 mg/m3 | |
TWA 0.1 mg/m3 | |
Nitric acid | TWA 2 ppm (5 mg/m3) ST 4 ppm (10 mg/m3) |
p-Nitroaniline | TWA 3 mg/m3 [skin] |
Nitrogen dioxide | ST 1 ppm (1.8 mg/m3) |
Nitroglycerine | ST 0.1 mg/m3) [skin] |
2-Nitropropane | TWA 10 ppm (35 mg/m3) |
Nitrotoluene (o-, m-, p-isomers) | TWA 2 ppm (11 mg/m3) [skin] |
Nonane | TWA 200 ppm (1050 mg/m3) |
Octachloronaphthalene | TWA 0.1 mg/m3 ST 0.3 mg/m3 [skin] |
Octane | TWA 300 ppm (1450 mg/m3) ST 375 ppm (1800 mg/m3) |
Osmium tetroxide (as Os) | TWA 0.002 mg/m3 (0.0002 ppm) ST 0.006 mg/m3 (0.0006 ppm) |
Oxalic acid | TWA 1 mg/m3 ST 2 mg/m3 |
Oxygen difluoride | C 0.05 ppm (0.1 mg/m3) |
Ozone | TWA 0.1 ppm (0.2 mg/m3) ST 0.3 ppm (0.6 mg/m3) |
Paraffin wax fume | TWA 2 mg/m3 |
Paraquat | TWA 0.1 mg/m3 (resp) [skin] |
Pentaborane | TWA 0.005 ppm (0.01 mg/m3) ST 0.015 ppm (0.03 mg/m3) |
Pentaerythritol | TWA 10 mg/m3 (total) TWA 5 mg/m3 (resp) |
n-Pentane | TWA 600 ppm (1800 mg/m3) ST 750 ppm (2250 mg/m3) |
2-Pentanone | TWA 200 ppm (700 mg/m3) ST 250 ppm (875 mg/m3) |
Perchloryl fluoride | TWA 3 ppm (14 mg/m3) ST 6 ppm (28 mg/m3) |
Petroleum distillates (naphtha) | TWA 400 ppm (1600 mg/m3) |
Phenothiazine | TWA 5 mg/m3 [skin] |
Phenyl glycidyl ether | TWA 1 ppm (6 mg/m3) |
Phenylhydrazine | TWA 5 ppm (20 mg/m3) ST 10 ppm (45 mg/m3) [skin] |
Phenylphosphine | C 0.05 ppm (0.25 mg/m3) |
Phorate | TWA 0.05 mg/m3 ST 0.2 mg/m3 [skin] |
Phosdrin | TWA 0.01 ppm (0.1 mg/m3) ST 0.03 ppm (0.3 mg/m3) [skin] |
Phosphine | TWA 0.3 ppm (0.4 mg/m3) ST 1 ppm (1 mg/m3) |
Phosphoric acid | TWA 1 mg/m3 ST 3 mg/m3 |
Phosphorus oxychloride | TWA 0.1 ppm (0.6 mg/m3) |
Phosphorus pentasulfide | TWA 1 mg/m3 ST 3 mg/m3 |
Phosphorus trichloride | TWA 0.2 ppm (1.5 mg/m3) ST 0.5 ppm (3 mg/m3) |
Phthalic anhydride | TWA 6 mg/m3 (1 ppm) |
m-Phthalodinitrile | TWA 5 mg/m3 |
Picloram | TWA 10 mg/m3 (total) TWA 5 mg/m3 (resp) |
Piperazine dihydrochloride | TWA 5 mg/m3 |
Platinum metal (as Pt) | TWA 1 mg/m3 |
Portland cement | TWA 10 mg/m3 (total) TWA 5 mg/m3 (resp) |
Potassium hydroxide | TWA 2 mg/m3 |
Propargyl alcohol | TWA 1 ppm (2 mg/m3) [skin] |
Propionic acid | TWA 10 ppm (30 mg/m3) |
Propoxur | TWA 0.5 mg/m3 |
n-Propyl acetate | TWA 200 ppm (840 mg/m3) ST 250 ppm (1050 mg/m3) |
n-Propyl alcohol | TWA 200 ppm (500 mg/m3) ST 250 ppm (625 mg/m3) |
Propylene dichloride | TWA 75 ppm (350 mg/m3) ST 110 ppm (510 mg/m3) |
Propylene glycol dinitrate | TWA 0.05 ppm (0.3 mg/m3) |
Propylene glycol monomethyl ether | TWA 100 ppm (360 mg/m3) ST 150 ppm (540 mg/m3) |
Propylene oxide | TWA 20 ppm (50 mg/m3) |
n-Propyl nitrate | TWA 25 ppm (105 mg/m3) ST 40 ppm (170 mg/m3) |
Resorcinol | TWA 10 ppm (45 mg/m3) ST 20 ppm (90 mg/m3) |
Ronnel | TWA 10 mg/m3 |
Rosin core solder, pyrolysis products (as formaldehyde) | TWA 0.1 mg/m3 |
Rouge | TWA 10 mg/m3 (total) TWA 5 mg/m3 (resp) |
Silica, amorphous | TWA 6 mg/m3 TWA 0.1 mg/m3 (fused) |
Silica, crystalline (as respirable dust) | TWA 0.05 mg/m3 (cristobalite) TWA 0.05 mg/m3 (tridymite) TWA 0.1 mg/m3 (quartz) TWA 0.1 mg/m3 (tripoli) |
Silicon | TWA 10 mg/m3 (total) TWA 5 mg/m3 (resp) |
Silicon carbide | TWA 10 mg/m3 (total) TWA 5 mg/m3 (resp) |
Silicon tetrahydride | TWA 5 ppm (7 mg/m3) |
Soapstone | TWA 6 mg/m3 (total) TWA 3 mg/m3 (resp) |
Sodium azide | C 0.1 ppm (as HN3) [skin] C 0.3 mg/m3 (as NaN3) [skin] |
Sodium bisulfite | TWA 5 mg/m3 |
Sodium fluoroacetate | TWA 0.05 mg/m3 ST 0.15 mg/m3 [skin] |
Sodium hydroxide | C 2 mg/m3 |
Sodium metabisulfite | TWA 5 mg/m3 |
Stoddard solvent | TWA 525 mg/m3 (100 ppm) |
Styrene | TWA 50 ppm (215 mg/m3) ST 100 ppm (425 mg/m3) |
Subtilisins | ST 0.00006 mg/m3 [60-minute] |
Sulfur dioxide | TWA 2 ppm (5 mg/m3) ST 5 ppm (13 mg/m3) |
Sulfur monochloride | C 1 ppm (6 mg/m3) |
Sulfur pentafluoride | C 0.01 ppm (0.1 mg/m3) |
Sulfur tetrafluoride | C 0.1 ppm (0.4 mg/m3) |
Sulfuryl fluoride | TWA 5 ppm (20 mg/m3) ST 10 ppm (40 mg/m3) |
Sulprofos | TWA 1 mg/m3 |
Talc | TWA 2 mg/m3 (resp) |
Temephos | TWA 10 mg/m3 (total) TWA 5 mg/m3 (resp) |
Terphenyl (o-, m-, p-isomers) | C 5 mg/m3 (0.5 ppm) |
1,1,2,2-Tetrachloroethane | TWA 1 ppm (7 mg/m3) [skin] |
Tetrachloroethylene | TWA 25 ppm (170 mg/m3) |
Tetrahydrofuran | TWA 200 ppm (590 mg/m3) ST 250 ppm (735 mg/m3) |
Tetrasodium pyrophosphate | TWA 5 mg/m3 |
4,4'-Thiobis(6-tert-butyl-m-cresol) | TWA 10 mg/m3 (total) TWA 5 mg/m3 (resp) |
Thioglycolic acid | TWA 1 ppm (4 mg/m3) [skin] |
Thionyl chloride | C 1 ppm (5 mg/m3) |
Tin (organic compounds, as Sn) | TWA 0.1 mg/m3 [skin] |
Tin(II) oxide (as Sn) | TWA 2 mg/m3 |
Tin(IV) oxide (as Sn) | TWA 2 mg/m3 |
Titanium dioxide | TWA 10 mg/m3 |
Toluene | TWA 100 ppm (375 mg/m3) ST 150 ppm (560 mg/m3) |
Toluene-2,4-diisocyanate | TWA 0.005 ppm (0.04 mg/m3) ST 0.02 ppm (0.15 mg/m3) |
m-Toluidine | TWA 2 ppm (9 mg/m3) [skin] |
p-Toluidine | TWA 2 ppm (9 mg/m3) [skin] |
Tributyl phosphate | TWA 0.2 ppm (2.5 mg/m3) |
Trichloroacetic acid | TWA 1 ppm (7 mg/m3) |
1,2,4-Trichlorobenzene | C 5 ppm (40 mg/m3) |
Trichloroethylene | TWA 50 ppm (270 mg/m3) ST 200 ppm (1080 mg/m3) |
1,2,3-Trichloropropane | TWA 10 ppm (60 mg/m3) |
1,1,2-Trichloro-1,2,2-trifluoroethane | TWA 1000 ppm (7600 mg/m3) ST 1250 ppm (9500 mg/m3) |
Triethylamine | TWA 10 ppm (40 mg/m3) ST 15 ppm (60 mg/m3) |
Trimellitic anhydride | TWA 0.005 ppm (0.04 mg/m3) |
Trimethylamine | TWA 10 ppm (24 mg/m3) ST 15 ppm (36 mg/m3) |
1,2,3-Trimethylbenzene | TWA 25 ppm (125 mg/m3) |
1,2,4-Trimethylbenzene | TWA 25 ppm (125 mg/m3) |
1,3,5-Trimethylbenzene | TWA 25 ppm (125 mg/m3) |
Trimethyl phosphite | TWA 2 ppm (10 mg/m3) |
2,4,6-Trinitrotoluene | TWA 0.5 mg/m3 [skin] |
Triorthocresyl phosphate | TWA 0.1 mg/m3 [skin] |
Triphenylamine | TWA 5 mg/m3 |
Tungsten (insoluble compounds, as W) | TWA 5 mg/m3 ST 10 mg/m3 |
Tungsten (soluble compounds, as W) | TWA 1 mg/m3 ST 3 mg/m3 |
Tungsten carbide (cemented) | TWA 5 mg/m3 (as W) ST 10 mg/m3 (as W) TWA 0.05 mg/m3 (as Co) TWA 1 mg/m3 (as Ni) |
Uranium (insoluble compounds, as U) | TWA 0.2 mg/m3 ST 0.6 mg/m3 |
n-Valeraldehyde | TWA 50 ppm (175 mg/m3) |
Vanadium dust | TWA 0.05 mg V2O5/m3 (resp) |
Vanadium fume | C 0.05 mg V2O5/m3 |
Vinyl acetate | TWA 10 ppm (30 mg/m3) ST 20 ppm (60 mg/m3) |
Vinyl bromide | TWA 5 ppm (20 mg/m3) |
Vinyl cyclohexene dioxide | TWA 10 ppm (60 mg/m3) [skin] |
Vinylidene chloride | TWA 1 ppm (4 mg/m3) |
VM & P Naphtha | TWA 1350 mg/m3 (300 ppm) ST 1800 mg/m3 (400 ppm) |
Welding fumes | TWA 5 mg/m3 |
Wood dust (all wood dusts except Western red cedar) | TWA 5 mg/m3 ST 10 mg/m3 |
Wood dust (Western red cedar) | TWA 2.5 mg/m3 |
Xylene (o-, m-, p-isomers) | TWA 100 ppm (435 mg/m3) ST 150 ppm (655 mg/m3) |
m-Xylene alpha, alpha'-diamine | C 0.1 mg/m3 [skin] |
Xylidine | TWA 2 ppm (10 mg/m3) [skin] |
Zinc chloride fume | TWA 1 mg/m3 ST 2 mg/m3 |
Zinc oxide | TWA 5 mg/m3 (fume) ST 10 mg/m3 (fume) TWA 10 mg/m3 (total dust) TWA 5 mg/m3 (resp dust) |
Zinc stearate | TWA 10 mg/m3 (total) TWA 5 mg/m3 (resp) |
Zirconium compounds (as Zr) | TWA 5 mg/m3 ST 10 mg/m3 |