2,4-펜탄디온

Other Classes -> Aliphatic Ketones, Other

Flammable agents - 3rd degree

log Kow = 0.40

0.40

0.14

Pleasant odor

Mild ketone-like odor

0.975 at 68 °F (USCG, 1999) - Less dense than water; will float

0.9721 at 25 °C/4 °C

Bulk density = 8.1 lb/gal

Relative density (water = 1): 0.98

0.975

0.9721 @25 °C

Colorless or slightly yellow liquid

Mobile, colorless or yellowish liquid; when cooled, solidifies to lustrous, pearly spangles. The liquid is affected by light, turning brown and forming resins.

In water, 166,000 mg/L at 20 °C

One part dissolves in about 8 parts water

Fairly soluble in neutral water

Miscible with alcohol, ether, chloroform, benzene, acetone, glacial acetic acid

For more Solubility (Complete) data for Acetyl acetone (7 total), please visit the HSDB record page.

166 mg/mL at 20 °C

93 °F (USCG, 1999)

38 °C (100 °F) - closed cup

105 °F - open cup

93 °F (34 °C) (Closed cup)

34 °C c.c.

93 °F

284.7 °F at 760 mmHg (USCG, 1999)

138 °C

136.00 to 138.00 °C. @ 760.00 mm Hg

140 °C

284.7 °F

139 °C @760 [mm Hg]

Warning

H226: Flammable liquid and vapor [Warning Flammable liquids]

P210, P233, P240, P241, P242, P243, P264, P270, P280, P301+P317, P303+P361+P353, P330, P370+P378, P403+P235, and P501 (click each P-code to see the statement)

Danger

H226 (100%): Flammable liquid and vapor [Warning Flammable liquids]

P210, P233, P240, P241, P242, P243, P261, P262, P264, P270, P271, P280, P301+P317, P302+P352, P303+P361+P353, P304+P340, P316, P321, P330, P361+P364, P370+P378, P403+P233, P403+P235, P405, and P501 (click each P-code to see the statement)

Chemical: 2,4-Pentanedione

Commission Regulation (EC) No 1565/2000 (Repealed by Com. Implementing Reg. (EU) No 872/2012)

2,4-Pentanedione is listed on the EPA's Chemical Data Reporting (CDR) system. Manufacturers and importers of 2,4-Pentanedione are required to report information about their production and use of this chemical to the EPA under the Toxic Substances Control Act (TSCA). (40 eCFR Part 711)

SP - indicates a substance that is identified in a proposed Significant New Use Rule.

REACH registered substance: Pentane-2,4-dione (EC: 204-634-0)

2,4-Pentanedione: HSNO Approval: HSR001072 Approved with controls

Behavior in Fire: Vapor is heavier than air and may travel to a source of ignition and flash back. (USCG, 1999)

· HIGHLY FLAMMABLE: Will be easily ignited by heat, sparks or flames.

Flammable. Above 34 °C explosive vapour/air mixtures may be formed.

Flammable liquid when exposed to heat or flame.

Moderate fire risk.

Inhalation causes dizziness, headache, nausea, vomiting and loss of consciousness. Contact with liquid irritates eyes. (USCG, 1999)

· TOXIC; may be fatal if inhaled, ingested or absorbed through skin.

Causes narcosis with an oral LD50 of 575-1000 mg/kg in rats; Rats inhaling 650 ppm six hours five times weekly for 14 weeks show degenerative changes of the brain and thymus; No neurotoxicity at 307 ppm; [ACGIH] Inhalation of high concentrations causes narcosis; [CHEMINFO MSDS]

Excerpt from ERG Guide 131 [Flammable Liquids - Toxic]:

Use powder, foam, carbon dioxide. In case of fire: keep drums, etc., cool by spraying with water.

Fresh air, rest. Artificial respiration may be needed. Refer for medical attention.

Remove contaminated clothes. Rinse and then wash skin with water and soap.

First rinse with plenty of water for several minutes (remove contact lenses if easily possible), then refer for medical attention.

Rinse mouth. Induce vomiting (ONLY IN CONSCIOUS PERSONS!). Refer for medical attention .

· CALL 911. Then call emergency response telephone number on shipping paper. If shipping paper not available or no answer, refer to appropriate telephone number listed on the inside back cover.

· ELIMINATE all ignition sources (no smoking, flares, sparks or flames) from immediate area.

INHALATION: remove to fresh air; if victim is not breathing, give artificial respiration and then oxygen; call a physician.

General First Aid:

Vapors are heavier than air and will collect in low areas. Vapors may travel long distances to ignition sources and flashback. Vapors in confined areas may explode when exposed to fire. Containers may explode in fire. Storage containers and parts of containers may rocket great distances, in many directions.

· Wear positive pressure self-contained breathing apparatus (SCBA).

20.0 [ppm]

Suitable extinguishing media: Dry powder, dry sand. Unsuitable extinguishing media: Do NOT use water jet.

Advice for firefighters: Wear self-contained breathing apparatus for firefighting if necessary.

When 2,4-pentanedione was incubated with yeast cells, no chromosome loss occurred even at a concentration of 1.96% (v/v) and cold shock, but the addition of propionitrile to the incubation mixture stimulated chromosomal loss.

... Acetylacetone inhibited the mutagenicity of 2-naphthohydroxamic acid.

LC50; Species: Pimephales promelas (fathead minnow); Concentration: 200 mg/L for 24 hr /Conditions of bioassay not specified in source examined/

LC50; Species: Pimephales promelas (fathead minnow); Conditions: flow-through, Lake Superior water, 25.2 °C, 6.3 dissolved oxygen, Hardness 46.5 mg/L CaCO3, pH 7.37; Concentration: 104 mg/L for 96 hr (95% confidence interval: 98.3-110 mg/L)... /Purity >99%/

LC50; Species: Pimephales promelas (fathead minnow); Conditions: flow-through, temperature 18.6 to 19.4 °C, pH 7.65 to 7.94, dissolved oxygen (DO) 6.19 to 9.22 mg/L, hardness (CaCO3) 196 mg/L; Concentration: 141 mg/L for 96 hr /Purity > 99%/

LC50; Species: Pimephales promelas (fathead minnow) 28 to 34 days-old; Conditions: flow-through with 99% replacement in about 2 hr; dissolved oxygen 7.57 mg/L, pH 7.32, 43.2 mg/L CaCO3, temperature 24 to 26 °C; Concentration: 142 mg/L for 96 hr /Purity >99%/

For more Ecotoxicity Values (Complete) data for Acetyl acetone (72 total), please visit the HSDB record page.

TERRESTRIAL FATE: Based on a classification scheme(1), an estimated Koc value of 34(SRC), determined from a log Kow of 0.40(2) and a regression-derived equation(3), indicates that acetyl acetone is expected to have very high mobility in soil(SRC). Volatilization of acetyl acetone from moist soil surfaces is expected to be an important fate process(SRC) given an estimated Henry's Law constant of 2.4X10-6 atm-cu m/mole(SRC) derived from its vapor pressure, 2.96 mm Hg(4), and water solubility, 166,000 mg/L(5). Acetyl acetone is expected to volatilize from dry soil surfaces(SRC) based upon its vapor pressure(4). Utilizing the Japanese MITI test, 83% of the Theoretical BOD was reached in 4 weeks(6), suggesting that biodegradation may be an important environmental fate process in soil(SRC).

AQUATIC FATE: Based on a classification scheme(1), an estimated Koc value of 34(SRC), determined from a log Kow of 0.40(2) and a regression-derived equation(3), indicates that acetyl acetone is not expected to adsorb to suspended solids and sediment(SRC). Volatilization from water surfaces is expected(4) based upon an estimated Henry's Law constant of 2.4X10-6 atm-cu m/mole(SRC), derived from its vapor pressure, 2.96 mm Hg(5), and water solubility, 166,000 mg/L(6). Using this Henry's Law constant and an estimation method(3), volatilization half-lives for a model river and model lake are 16 days and 120 days, respectively(SRC). The aquatic oxidation rate for acetyl acetone has been experimentally determined to be 9.9X10-9 L/mol-s at pH 6.4(7). Based on this rate and a hydroxyl radical concentration of 1X10-17 mol/L in water under continuous sunlight(8), the half-life for the aquatic oxidation of acetyl acetone can be estimated to be 81 days(SRC). According to a classification scheme(9), an estimated BCF of 3(SRC), from its log Kow(2) and a regression-derived equation(3), suggests the potential for bioconcentration in aquatic organisms is low(SRC). Utilizing the Japanese MITI test, 83% of the Theoretical BOD was reached in 4 weeks(10), suggesting that biodegradation may be an important environmental fate process in water(SRC).

Section 8(a) of TSCA requires manufacturers of this chemical substance to report preliminary assessment information concerned with production, exposure, and use to EPA as cited in the preamble in 51 FR 41329. Effective date: 9/30/91; Reporting date: 11/27/91.

Pursuant to section 8(d) of TSCA, EPA promulgated a model Health and Safety Data Reporting Rule. The section 8(d) model rule requires manufacturers, importers, and processors of listed chemical substances and mixtures to submit to EPA copies and lists of unpublished health and safety studies. 2,4-Pentanedione is included on this list. Effective date: 9/30/91; Sunset date: 12/19/95.

2,4-Pentanedione (2,4-PD; CAS No. 123-54-6) ... was investigated for its comparative pharmacokinetics in male Fischer 344 rats by a single intravenous (i.v.) injection of (4.3, 43, 148.5, and 430 mg/kg), or a 6-hr nose-only inhalation exposure (400 ppm) to (14)C-2,4-PD. For the i.v. route, the plasma concentration of (14)C-2,4-PD-derived radioactivity declined in a biexponential fashion. The overall form of the (14)C plasma concentration-time curves and derived pharmacokinetic parameters indicated that dose-linear kinetics occurred in the i.v. dose range 4.3-148.5 mg/kg, but not with 430 mg/kg. Metabolism of 2,4-PD was rapid to undetectable after 8 hr. (14)C-2,4-PD derived radioactivity was eliminated mainly as (14)CO2 and in urine. For the 4.3, 43 and 148.5 mg/kg doses (14)CO2 elimination was relatively constant (36.8, 38.8 and 42.3% in 48 hr samples respectively) and greater than urinary excretion (17.9, 14.3 and 29.6%; 48 hr specimens). At 430 mg/kg i.v. there was a reversal of the excretion pattern, with urine (14)C excretion (54.7%) becoming greater than that for (14)CO2 (27.3%). Excretion in expired volatiles and feces was small. Radiochromatograms of urine showed free 2,4-PD in the 12 hr sample, together with 7 other metabolites. Free 2,4-PD and 6 of the metabolites decreased or were not detectable in a 24 or 48 hr urine sample, but one peak (retention 7.9 min) increased progressively to become the major fraction (97%). Nose-only exposure to 400 ppm (14)C-2, 4-PD produced a mean decrease in breathing rate of 20.1%, which was constant and sustained throughout exposure, due to a lengthening of the expiratory phase of the respiratory cycle. (14)C-2,4-PD was rapidly absorbed during the first 3 hr of exposure, then began to plateau, but did not reach a steady state. Postexposure elimination of (14)C from plasma followed a biexponential form with a t1/2 for the terminal disposition phase of 30.72 hr. ... Postexposure, plasma unmetabolized 2,4-PD declined rapidly to undetectable concentrations by 12 hr. Radiolabel excretion was approximately equivalent in urine (37.6%) and expired (14)CO2 (36.3%). Urine radiochromatograms showed a minor 2,4-PD contaminant (0.6-5.9% over 48 hr), along with 7 other peaks probably representing metabolites. The major metabolite peak was at 7.8 min retention, increasing from 41.1% (12 hr) to 62.8% (48 hr). Immediately postexposure, radioactivity was present in all tissues examined, but on a concentration basis (microgram equiv/g) there was no preferential accumulation of (14)C in any tissue or organ. ...

Used as a chemical intermediate, solvent, metal chelating agent, lubricant additive, and pesticide; [Hawley] Used as a metal chelator, lubricant additive, corrosion inhibitor, polyolefin modifier, and intermediate; [ACGIH]

Painting (Solvents) [Category: Paint]

Forms organometallic complexes which are used as gasoline additives, lubricant additives, driers for varnishes and printer's inks ... .

Fungicides, insecticides, colors /SRP: Former uses/

Solvent for cellulose acetate, intermediate, chelating agent for metals, paint driers, lubricant additives.

2,4-Pentanedione is used as an intermediate, in particular for the synthesis of heterocyclic substances for biologically active compounds and dyes, and for the production of metal acetylacetonates. Furthermore, 2,4-pentanedione is used as a solvent, and as an absorption and extraction agent, particularly for the separation and purification of metal ions. Another application is for the purification of metal-containing wastewater and for corrosion protection. 2,4-Pentanedione is also used as a component of catalyst systems for polymerization, copolymerization, oligo- and dimerization.

2023: 1,000,000 - <2,500,000 lb

This chemical is listed as a High Production Volume (HPV) (65FR81686). Chemicals listed as HPV were produced in or imported into the U.S. in >1 million pounds in 1990 and/or 1994. The HPV list is based on the 1990 Inventory Update Rule. (IUR) (40 CFR part 710 subpart B; 51FR21438).

(1972) PROBABLY GREATER THAN 4.54X10+5 GRAMS

(1975) GREATER THAN 9.08X10+5 GRAMS

Production volumes for non-confidential chemicals reported under the Inventory Update Rule. [Table#3821]

Non-confidential 2016 Chemical Data Reporting (CDR) information on the production and use of chemicals manufactured or imported into the United States. Chemical: 2,4-Pentanedione:

2,4-Pentanedione is produced by thermal or metal-catalyzed rearrangement of isopropenyl acetate (obtained from acetone and ketene). Isopropenyl acetate vapor is fed at atmospheric pressure through a V2A steel tube with an inner temperature of 520 °C. The hot reaction gases are quenched, condensed, and cooled to 20 °C, whereby the gaseous byproducts carbon monoxide, carbon dioxide, methane, and ketene are separated. The product is purified by fractional distillation. Other industrially less important processes for the production of 2,4-pentanedione, include the Claisen ester condensation of ethyl acetate with acetone using sodium ethoxide as condensation agent and the acetylation of acetoacetic acid esters with acetic anhydride in the presence of magnesium salts.