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EC number: 203-738-3 | CAS number: 110-13-4
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Dermal absorption
Administrative data
- Endpoint:
- dermal absorption in vivo
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Study period:
- 1987
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Study well documented, meets generally accepted scientific principles, acceptable for assessment
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 1 987
- Report date:
- 1987
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- GLP compliance:
- not specified
Test material
- Reference substance name:
- Hexane-2,5-dione
- EC Number:
- 203-738-3
- EC Name:
- Hexane-2,5-dione
- Cas Number:
- 110-13-4
- Molecular formula:
- C6H10O2
- IUPAC Name:
- hexane-2,5-dione
- Test material form:
- not specified
- Details on test material:
- 2,5-[ 1,2,5,6-14C]Hexanedione, specific activity of 5. 1 mCi/
mmol, was prepared by Amersham Corp., Arlington Heights, IL. Radiochemical
purity was determined by gas-liquid chromatography to be
97%. 2,5-Hexanedione (2,5-HD, 98% pure) was obtained from Eastman
Kodak Co., Rochester, NY. 2,5-Dimethylfuran (99%) was purchased
from Aldrich Chemical Co., Milwaukee, WI. 5-Hydroxy-2-hexanone was
a gift from Dr. G. D. DiVincenzo, Eastman Kodak Company, Rochester
NY. Amberlite XAD-4 resin was obtained from Supelco Inc., Bellefonte,
PA. All other chemicals used in this study were obtained in the highest
purity available.
Constituent 1
- Radiolabelling:
- yes
- Remarks:
- 14 C
Test animals
- Species:
- hen
- Strain:
- other: Gallus gallus domesticus
- Sex:
- female
- Details on test animals or test system and environmental conditions:
- Laying hens (Gallus gallus domesticus),
18 months old with average weights of 1.6 ± 0.04 kg (mean ± SE), were
obtained from Featherdown Farm, Raleigh, NC. Fifteen hens were each
given a dermal dose of 50 mg (7.5 uCi) of 2,5-HD/kg of body weight.
To avoid evaporation of 2,5-HD, the dose was injected through a rubber
septum that was attached to a round glass vial (2.5 cm in diameter) glued
over the midthoracic region of the chicken. The birds were housed in
individual metabolism cages (1 .5 x 2.5 feet, custom-made), which were
made of glass and contained coarse-mesh screens to isolate excrement.
The cages were placed in a temperature-controlled room (2 1-23#{176}wC)ith
a I 2-hr light cycle and free access to feed (Layena chicken feed, Ralston
Purina Co., St. Louis, MO) and water. Two consecutive traps were
connected to the metabolism cages. The first contained 50 g of Amberlite
XAD-4 to trap volatile organic compounds (20-22), and the second trap
had 250 ml of a mixture of ethanolamine:ethylene glycol monomethyl
ether (1:2 v/v) to collect 14C02. The Amberlite XAD-4 trap and carbon
dioxide trap were collected at 2, 4, 8, and 24 hr following treatment,
while excreta and eggs were collected daily. Three treated hens were
killed at each of the following time points: 4, 8, 24, 36, and 48 hr. In
addition, two hens were killed 2 hr following dosing to further determine
the peak distribution of 2,5-HD. Birds were anesthetized with an intraperitoneal
injection ofsodium pentobarbital solution (Nembutal, Abbott
Laboratories, North Chicago, IL). The blood was collected by a heparinized
syringe via heart puncture and centrifuged to separate plasma from
red blood cells. Individual organs and tissues were removed and weighed.
Skin and adipose tissue samples were obtained from three sites, one from
the anterior portion ofeach thigh and one from the thorax. Spinal cords
were sampled at three sites, with one sample from each site (cervical,
thoracic, and sacral segments). The contents of the gastrointestinal tract
parts, e.g. crop, proventriculus, ventriculus, small intestine, ceca and
large intestine, were collected and homogenized separatetely.
Administration / exposure
- Type of coverage:
- occlusive
- Vehicle:
- unchanged (no vehicle)
- Duration of exposure:
- To avoid evaporation of 2,5-HD, the dose was injected through a rubber septum that was attached to a round glass vial (2.5 cm in diameter) glued over the midthoracic region of the chicken. Three treated hens were killed at each of the following time points: 4, 8, 24, 36, and 48 hr. In addition, two hens were killed 2 hr following dosing to further determine the peak distribution of 2,5-HD.
- Doses:
- dermal dose of 50 mg (7.5 µCi) of 2,5-HD/kg of body weight
- No. of animals per group:
- Fifteen hens
- Control animals:
- no
Results and discussion
- Signs and symptoms of toxicity:
- no effects
- Dermal irritation:
- not examined
- Total recovery:
- The disappearance of 2,5-HD from the dosing site of treated hens followed a monoexponential kinetics with a half-life of 6.09 hr. By the end of the experiment, only 0.41 % of the radioactive dose was recovered from the dosing site.
Applicant's summary and conclusion
- Conclusions:
- The disappearance of 2,5-HD from the dosing
site of treated hens followed a monoexponential kinetics
with a half-life of 6.09 hr. By the end of the experiment, only
0.41% of the radioactive dose was recovered from the dosing
site.
2,5-Hexanedione (2,5-HD) was readily absorbed from the skin
of the treated hen as indicated by its disappearance from the
dosing site and the concurrent detection of radioactivity in the
plasma and all tissues analyzed.
2,5-HD was the predominant compound present in liver,
lungs, and kidneys at 4- and 24-hr time points. Again, this is
probably due to the high rate of excretion of 5-hydroxy-2-
hexanone and/or its oxidation to 2,5-HD by these tissues.
This study concludes that 2,5-HD is metabolized in the hen
to 5-hydroxy-2-hexanone and 2,5-dimethylfuran which are common
metabolites of some other aliphatic hexacarbons. 2,5-HD
is readily absorbed from the skin and subsequently distributed
throughout the body of the hen. Low concentrations of radioactivity
were observed in the target tissues, i. e. the neural tissues,
after a single administration. - Executive summary:
A dermal dose of 50 mg/kg (7.5 MCi/kg) of [14C]2,5-hexanedione (2,5-HD) was applied on a protected area on the backs of hens. Five groups of three hens were killed after 4, 8, 24, 36, and 48 hr. 2,5-HD disappeared monoexponentially from the application sfte with a halflife of 6 hr. After 48 hr, 35% of the radioactivfty was expired as volatile material, largely as 2,5-HD. The combined urinary fecal excreta accounted for 15% of the eliminated radioactivity, while the 14CO2 accounted for 11.9% of the radioactive dose. The highest concentration of 14C was detected in the bile. Among tissues analyzed, liver and kidney contained the highest concentrations of radioactivfty, whereas the brain, spinal cord, and peripheral nerves showed smaller concentrations. The half-lives for the elimination of 14C were longest for muscle (71 hr) and shortest for adipose tissue (12 hr), while the remaining tissues showed half-lives ranging from 20 to 30 hr. Radioactivfty in the plasma reached a peak at 4 hr. Most of this radioactivity was identified as 5-hydroxy-2-hexanone followed by 2,5-HD and 2,5-dimethylfuran; these chemicals then disappeared biexponentially with terminal half-lives of 7.6 hr, 12.6 hr, and 28.6 hr, respectively. 2,5-HD was the most accounted chemical found in the liver, lung, and kidney, while 5-hydroxy-2-hexanone was found to be most abundant in the combined urinary-focal excreta.
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