Acrylonitrile
May 1994
Immediately Dangerous to Life or Health Concentrations (IDLH)
CAS number: 107-13-1
NIOSH REL: 1 ppm TWA, 10 ppm 15-minute CEILING [skin]; NIOSH considers acrylonitrile to be a potential occupational carcinogen as defined by the OSHA carcinogen policy [29 CFR 1990].
Current OSHA PEL: 2 ppm TWA, 10 ppm 15-minute CEILING [skin]
1989 OSHA PEL: Same as current PEL
1993-1994 ACGIH TLV: 2 ppm (4.3 mg/m3) TWA [skin], A2
Description of substance: Colorless to pale-yellow liquid with an unpleasant odor.
LEL: 3.0% (10% LEL, 3,000 ppm)
Original (SCP) IDLH: 500 ppm
Basis for original (SCP) IDLH: The chosen IDLH is based on the statement by Spector [1956] about a rat 4-hour LC50 of 500 ppm [Carpenter et al. 1949].
Short-term exposure guidelines: None developed
ACUTE TOXICITY DATA
Lethal concentration data:
Adjusted | ||||||
---|---|---|---|---|---|---|
LC50 | LCLo | 0.5-hr | Derived | |||
Species | Reference | (ppm) | (ppm) | Time | LC (CF) | Value |
Rat | Carpenter et al. 1949 | 500 | —– | 4 hr | 3,635 ppm (7.27) | 364 ppm |
Rabbit | Dudley and Neal 1942 | —– | 260 | 4 hr | 1,890 ppm (7.27) | 189 ppm |
G. pig | Dudley and Neal 1942 | —– | 575 | 4 hr | 4,180 ppm (7.27) | 418 ppm |
Mouse | Dudley and Neal 1942 | 313 | —– | 4 hr | 2,276 ppm (7.27) | 228 ppm |
Rat | Jaeger et al. 1974 | 425 | —– | 4 hr | 3,090 ppm (7.27) | 309 ppm |
Rat | Patty 1963 | —– | 636 | 4 hr | 4,624 ppm (7.27) | 462 ppm |
Human | Schwanecke 1966 | —– | 452 | 1 hr | 850 ppm (1.88) | 85 ppm |
*Note: Conversion factor (CF) was determined with “n” = 1.1 [ten Berge et al. 1986].
Other human data: None relevant for use in determining the revised IDLH.
Revised IDLH: 85 ppmBasis for revised IDLH: The revised IDLH for acrylonitrile is 85 ppm based on acute inhalation toxicity data in humans [Schwanecke 1966]. [Note: NIOSH recommends as part of its carcinogen policy that the “most protective” respirators be worn for acrylonitrile at concentrations above 1 ppm. OSHA currently requires in 29 CFR 1919.1045 that workers be provided with and required to wear and use the “most protective” respirators in concentrations exceeding 4,000 ppm (i.e., 2,000 x the PEL).] |
References:
- Carpenter CP, Smyth HF Jr, Pozzani UC [1949]. The assay of acute toxicity, and the grading and interpretation of results of 96 chemical compounds. J Ind Hyg Toxicol 31(6):344.
- Dudley HC, Neal PA [1942]. Toxicology of acrylonitrile (vinyl cyanide). A study of the acute toxicity. J Ind Hyg Toxicol 24(2):27-36.
- Jaeger RJ, Conolly RB, Murphy SD [1974]. Toxicity and biochemical changes in rats after inhalation exposure to 1.1-dichloroethylene, bromobenzene, styrene, acrylonitrile or 2-chlorobutadiene. (Abstract for Thirteenth Annual Meeting of the Society of Toxicology, Washington, DC, March 10-14, 1974.) Toxicol Appl Pharmacol 29:81.
- Patty FA, ed. [1963]. Industrial hygiene and toxicology. 2nd rev. ed. Vol. II. Toxicology. New York, NY: Interscience Publishers, Inc., pp. 2009-2011.
- Schwanecke R [1966]. Safety hazards in the handling of acrylonitrile and methacrylonitrile. Zentralbl Arbeitsmed Arbeitsschutz 16(1):1-3 (in German).
- Spector WS, ed. [1956]. Handbook of toxicology. Vol. I. Acute toxicities of solids, liquids and gases to laboratory animals. Philadelphia, PA: W.B. Saunders Company, pp. 322-323.
- ten Berge WF, Zwart A, Appelman LM [1986]. Concentration-time mortality response relationship of irritant and systematically acting vapours and gases. J Haz Mat 13:301-309.