NIOSH REL: None established; NIOSH considers pnitrochlorobenzene to be a potential occupational carcinogen as defined by the OSHA carcinogen policy [29 CFR 1990] that may be absorbed through the skin.
Current OSHA PEL: 1 mg/m3 TWA [skin]
1989 OSHA PEL: Same as current PEL
1993-1994 ACGIH TLV: 0.64 mg/m3 (0.1 ppm) TWA [skin]
Description of substance: Yellow, crystalline solid with a sweet odor.
LEL: . . . Unknown
Original (SCP) IDLH: 1,000 mg/m3
Basis for original (SCP) IDLH: No data on acute inhalation toxicity are available on which to base an IDLH for pnitrochlorobenzene. The chosen IDLH, therefore, is based on an analogy with nitrobenzene, which has an IDLH of 200 ppm. [Note: A concentration of 200 ppm nitrobenzene is equivalent to about 1,000 mg/m3 pnitrochlorobenzene.]
Short-term exposure guidelines: None developed
ACUTE TOXICITY DATA:
Lethal concentration data:
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Cat | Watrous & Schultz 1950 |
Lethal dose data:
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Rat | Back et al. 1972 | |||||
Mouse | Back et al. 1972 | |||||
Mouse | Izmerov et al. 1982 | |||||
Rat | Sziza & Magos 1959 |
Other animal data: Exposures of cats and guinea pigs to 87 mg/m3 for 8 hours/day for 6 weeks resulted in methemoglobinemia and slight anemia [Watrous and Schultz 1950].
Human data: Workers exposed intermittently for 0.5 to 1 hour
over many months to concentrations ranging from 7 to 400 mg/m3
(average of 90 mg/m3) had only vague complaints
of tiredness, loss of appetite, headache, and afternoon fatigue
[Watrous and Schultz 1950]. Because of the strong and disagreeable
odor, these workers voluntarily wore respiratory protection when
exposed to the higher concentrations [Watrous and Schultz 1950].
Revised IDLH: 100 mg/m3
Basis for revised IDLH: The revised IDLH for pnitrochlorobenzene is 100 mg/m3 based on subchronic inhalation toxicity data in workers [Watrous and Schultz 1950] and animals [Watrous and Schultz 1950]. This may be a conservative value due to the lack of relevant acute toxicity data for workers exposed to concentrations above 100 mg/m3. [Note: NIOSH recommends as part of its carcinogen policy that the "most protective" respirators be worn for pnitrochlorobenzene at any detectable concentration.] |
REFERENCES:
1. Back KC, Thomas AA, MacEwen JD [1972]. Reclassification of materials listed as transportation health hazards. WrightPatterson Air Force Base, OH: 6570th Aerospace Medical Research Laboratory, Report No. TSA20723, pp. A270 to A271.
2. Izmerov NF, Sanotsky IV, Sidorov KK [1982]. Toxicometric parameters of industrial toxic chemicals under single exposure. Moscow, Russia: Centre of International Projects, GKNT, p. 92.
3. Sziza M, Magos I [1959]. Toxikologische untersuchung einiger in der ungarischen industrie zur anwendung gelangenden aromatischen nitroverbindungen. Arch Gewerbepath Gewerbehyg 17:217226 (in German).
4. Watrous RM, Schultz HN [1950]. Cyclohexylamine, pchloronitrobenzene,
2aminopyridine: toxic effects in industrial use. Ind Med
Surg 19:317320.
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