NIOSH REL: 6 mg/m3 (1 ppm) TWA
Current OSHA PEL: 12 mg/m3 (2 ppm) TWA
1989 OSHA PEL: 6 mg/m3 (1 ppm) TWA
1993-1994 ACGIH TLV: 6.1 mg/m3 (1 ppm) TWA
Description of substance: White solid (flake) or a clear, colorless, mobile liquid (molten) with a characteristic, acrid odor.
LEL: . . 1.7% (10% LEL, 10,500 mg/m3)
Original (SCP) IDLH: 10,000 mg/m3
Basis for original (SCP) IDLH: Because no data on acute inhalation toxicity are available on which to base an IDLH for phthalic anhydride, the chosen IDLH is based on repeated exposure data. AIHA [1967] reported that exposure of rats and rabbits to 10,000 mg/m3 for 4 hours/day for several days produced a 25% fatality rate [Malten and Zielhuis 1964].
Short-term exposure guidelines: None developed
ACUTE TOXICITY DATA:
Lethal dose data:
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| |||||
Rat | Biofax 1970 | |||||
Mouse | Izmerov et al. 1982 | |||||
Cat | Marhold 1986 | |||||
Rat | Patty 1963 | |||||
Mouse | Zhilova & Kasparov 1969 |
Other animal data: It has been reported that exposure of
rats and rabbits to 10,000 mg/m3 for 4 hours/day
for several days produced a 25% fatality rate [Malten and Zielhuis 1964].
Human data: It has been reported that an exposure of 30 mg/m3
is associated with conjunctivitis, while 25 mg/m3
is associated with signs of mucous membrane irritation [Baader
1955]. It has been stated that phthalic anhydride has similar
toxic effects (i.e., irritation of the skin, eyes, and upper respiratory
system) as maleic anhydride, but has reduced potency [ACGIH 1991].
Revised IDLH: 60 mg/m3
Basis for revised IDLH: Based on acute toxicity data in animals [Biofax 1970; Izmerov et al. 1982; Malten and Zielhuis 1964; Marhold 1986; Patty 1963; Zhilova and Kasparov 1969], a value between 600 and 3,000 mg/m3 would have been appropriate. However, the revised IDLH for phthalic anhydride is 60 mg/m3 (i.e., 10 times the NIOSH REL) based on acute inhalation data in humans [Baader 1955] and an analogy to maleic anhydride [ACGIH 1991] which has a revised IDLH that is 10 times its NIOSH REL. This may be a conservative value due to the lack of relevant acute toxicity data for workers exposed to concentrations above 30 mg/m3. |
REFERENCES:
1. ACGIH [1991]. Phthalic anhydride. In: Documentation of the threshold limit values and biological exposure indices. 6th ed. Cincinnati, OH: American Conference of Governmental Industrial Hygienists, pp. 12631264.
2. AIHA [1967]. Phthalic anhydride. In: Hygienic guide series. Am Ind Hyg Assoc J 28:395398.
3. Baader EW [1955]. Diseases due to phthalic acid and its compounds. Arch Gewerbepath Gewerbehyg 13:419453 (in German).
4. Biofax [1970]. Phthalic anhydride. Northbrook, IL: Biofax Industrial BioTest Laboratories, Inc.
5. Izmerov NF, Sanotsky IV, Sidorov KK [1982]. Toxicometric parameters of industrial toxic chemicals under single exposure. Moscow, Russia: Centre of International Projects, GKNT, p. 322.
6. Malten KE, Zielhuis RL [1964]. Alkyd resins. In: Industrial toxicology and dermatology in the production and processing of plastics. Amsterdam, The Netherlands: Elsevier Publishing Company, pp. 5970.
7. Marhold J [1986]. Prehled Prumyslove Toxikologie, Organicke Latky. Prague, Czechoslovakia: Avicenum, p. 322 (in Czechoslovakian).
8. Patty FA, ed. [1963]. Industrial hygiene and toxicology. 2nd rev. ed. Vol. II. Toxicology. New York, NY: Interscience Publishers, Inc., pp. 18221823.
9. Zhilova NA, Kasparov AA [1969]. Phthalic anhydride and nnitrosodiphenylamine
(Vulcalent A). Chem Abstr 71:280.
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