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EC number: 240-106-6 | CAS number: 15968-01-1
- 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
Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics in vivo
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: No OECD guideline or GLP defined.
Data source
Reference
- Reference Type:
- publication
- Title:
- Toxicokinetics of Phthalic Acid: The Common Final Metabolite of Phthalic Acid Esters in Rats
- Author:
- Lim DS, Shin BS, Yoo SD, Kim HS, Kwack SJ, Ahn MY, Lee BM
- Year:
- 2 007
- Bibliographic source:
- Journal of Toxicology and Environmental Health, Part A, 70: 1344–1349
Materials and methods
- Objective of study:
- toxicokinetics
- Principles of method if other than guideline:
- The toxicokinetic profiles of phthalic acid (PA) were studied in rats after orally administering doses 20, 100, or 500 mg/kg. Concentrations of PA were determined in serum or urine by high performance liquid chromatography (HPLC).
- GLP compliance:
- not specified
Test material
- Reference substance name:
- Phthalic acid
- EC Number:
- 201-873-2
- EC Name:
- Phthalic acid
- Cas Number:
- 88-99-3
- IUPAC Name:
- phthalic acid
Constituent 1
- Radiolabelling:
- not specified
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Samtako, Inc. (Seoul, Korea)
- Age at study initiation: Seven-week-old male rats.
- Housing: After dosing, animals were housed in metabolic cages.
- Diet (e.g. ad libitum): standard rat diet (Samtako, Inc.), ad libitum
- Water (e.g. ad libitum): ad libitum
- Acclimation period: One week
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 23 ± 2°C
- Humidity (%): 50 ± 10%
- Photoperiod (hrs dark / hrs light): 12-h light/dark cycle
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- corn oil
- Duration and frequency of treatment / exposure:
- Single administration of the test substance
Doses / concentrations
- Remarks:
- Doses / Concentrations:
20, 100, or 500 mg/kg
- No. of animals per sex per dose / concentration:
- Three males per dose
- Control animals:
- no
- Details on dosing and sampling:
- For each dosage group, studies were conducted over 3 d, and plasma samples were collected at 30 min, 1, 2, 3, 4, 6, 8, 12, and 24 h postadministration.
Pooled urine from each rat was collected in a glass vial from 0–4, 4–8, 8–12, 12–16, and 16–24 h after dosing.
Results and discussion
Toxicokinetic / pharmacokinetic studies
- Details on absorption:
- The test substance was absorbed rapidly after an oral dose of 500 mg/kg with peak concentration (Cmax) in blood (3.5 ± 0.33 ug/ml) at 30 min postadministration. After oral administration, the dose-normalized area under the curve (AUC) (146.90 ± 9.33 mg/h/ml) for 500 mg/kg was significantly greater than at 20
mg/kg (44.69 ± 2.56 mg/h/ml). - Details on distribution in tissues:
- The plasma concentrations of the test substance showed a biexponential increase following oral administration of doses ranging from 20 to 500 mg/kg. The terminal elimination half-lives (t1/2) of test substance at dosages of 20, 100, or 500 mg/kg were 6.46 ± 1.13, 5.19 ± 3.56, and 5.10 ± 1.10 h, respectively, total clearances (Cl/F) of test substance at 20, 100, or 500 mg/kg were 97.43 ± 4.20, 215.01 ± 55.42, and 721.07 ± 51.81 ml/h, and apparent distribution volumes of test substance in the steady state (Vz/F) at 20, 100, or 500 mg/kg were 903.28 ± 125.28, 1419.87 ± 527.53, and 5264.86 ± 993.65 ml, respectively.
- Details on excretion:
- The main route of elimination following a single p.o. dose of test substance was in urine. After administering oral doses of 20,100, or 500 mg/kg bw, the test substance was excreted in urine within 24h. A larger percentage (13-26%) of test substance was excreted in urine following a single oral administration (20-500 mg/kg bw). The results show that test substance plasma levels in rats declined in a biphasic fashion after oral administration. The apparent distribution volume in the steady state indicates that test substance is distributed extensively into tissues. The total systemic clearance of test substance was moderate and significantly less than hepatic blood flow (approximately 3.91 h/kg). The test substance was absorbed rapidly after oral administration, and peak plasma concentrations were attained 30 min after administration. Urine analysis after the oral administration at 500 mg/kg indicated that only about 13% of unchanged test substance is excreted in urine. In conclusion, the present investigation demonstrates that test substance concentrations in rat plasma declined following oral administration with a mean terminal elimination half-life of about 5-6h
Toxicokinetic parametersopen allclose all
- Toxicokinetic parameters:
- half-life 1st: 5-6 h [20 mg/kg]
- Toxicokinetic parameters:
- Tmax: 0.83 ± 0.29 (h) [20 mg/kg]
- Toxicokinetic parameters:
- Cmax: 4.92 ± 0.78 (µg/ml) [20 mg/kg]
- Toxicokinetic parameters:
- AUC: (µg-h/ml) 44.69 ± 2.56 [20 mg/kg]
- Toxicokinetic parameters:
- half-life 1st: 5.19 ± 3.56 (h) [100 mg/kg]
- Toxicokinetic parameters:
- Tmax: 1.00 ± 0.87 (h) [100 mg/kg]
- Toxicokinetic parameters:
- Cmax: 15.87 ± 1.68 (µg/ml) [100 mg/kg]
- Toxicokinetic parameters:
- AUC: (µg-h/ml) 107.64 ± 31.77 [100 mg/kg]
- Toxicokinetic parameters:
- half-life 1st: 5.10 ± 1.19 (h) [500 mg/kg]
- Toxicokinetic parameters:
- Tmax: 0.67 ± 0.29 (h) [500 mg/kg]
- Toxicokinetic parameters:
- Cmax: 20.49 ± 3.64 (µg/ml) [500 mg/kg]
- Toxicokinetic parameters:
- AUC: (µg-h/ml) 146.90 ± 9.33 [500 mg/kg]
Metabolite characterisation studies
- Metabolites identified:
- not specified
Any other information on results incl. tables
Concentration of Phthalic Acid (PA) in Urine Samples After Its Oral Administration to Male Rats:
Time interval (h) | Conc. (µg/ml) | Urine Volume (ml) | PA #1 (total amount excreted, µg) | Conc. (µg/ml) | Urine Volume (ml) | PA #2 (total amount excreted, µg) | Conc.(µg/ml) | Urine Volume (ml) | PA #3 (total amount excreted, µg) |
PA-500 mg/kg | |||||||||
0 -4 | 12492.67 | 1.0 | 12492.67 | 5814.89 | 2.0 | 11629.77 | 7306.40 | 2.0 | 14612.79 |
4 -8 | 9410 .84 | 2.4 | 22586.01 | 12149.83 | 2.0 | 24299.65 | 11642.85 | 1.8 | 20957.13 |
8 -12 | 6386.03 | 2.4 | 15326.47 | 5611.77 | 2.5 | 14029.43 | 5648.68 | 1.8 | 10167.62 |
12 -16 | 3713.82 | 1.8 | 6684.87 | 5319.60 | 2.0 | 10639.20 | 4379.18 | 1.8 | 7882.52 |
16 -24 | 3311.50 | 2.0 | 6622.99 | 1228.05 | 4.0 | 4912.18 | 1047.12 | 4.0 | 4188.48 |
PA-100 mg/kg | |||||||||
0 -4 | 4154.18 | 2.0 | 8308.35 | 5629.77 | 1.0 | 5629.77 | 4869.44 | 2.0 | 9738.87 |
4 -8 | 6369.44 | 2.0 | 12738.87 | 5639.02 | 2.5 | 14097.55 | 5425.86 | 2.5 | 13564.64 |
8 -12 | 1441.43 | 2.0 | 2882.86 | 2122.93 | 2.5 | 5307.33 | 1880.74 | 3.0 | 5642.21 |
12 -16 | 549.18 | 3.0 | 1647.54 | 1402.85 | 2.0 | 2805.70 | 681.56 | 2.5 | 1703.90 |
16 -24 | 170 .06 | 3.0 | 510.17 | 529.60 | 2.0 | 1059.19 | 248.59 | 4.5 | 1118.64 |
PA-20 mg/kg | |||||||||
0 -4 | 558.15 | 2.0 | 1116.3 | 503.30 | 2.0 | 1006.59 | 443.29 | 2.0 | 886.58 |
4 -8 | 375.97 | 2.5 | 939.92 | 313.06 | 2.5 | 782.65 | 380.94 | 2.0 | 761.87 |
8 -12 | 248.87 | 2.0 | 497.74 | 119.10 | 4.0 | 476.39 | 172.43 | 2.5 | 431.07 |
12 -16 | 138.78 | 2.5 | 346.94 | 158.34 | 2.0 | 316.68 | 70.28 | 4.0 | 281.10 |
16 -24 | 81.80 | 3.0 | 245.39 | 29.17 | 8.0 | 233.37 | 133.37 | 2.0 | 266.73 |
Applicant's summary and conclusion
- Executive summary:
The toxicokinetic profiles of phthalic acid (PA) were studied in rats after orally administering doses 20, 100, or 500 mg/kg. Concentrations of PA were determined in serum or urine by high performance liquid chromatography (HPLC). The plasma concentrations of PA showed a biexponential increase following oral administration of doses ranging from 20 to 500 mg/kg. The terminal
elimination half-lives (t1/2) of PA at dosages of 20, 100, or 500 mg/kg were 6.46 ± 1.13, 5.19 ± 3.56, and 5.10 ± 1.10 h, respectively,
total clearances (Cl/F) of PA at 20, 100, or 500 mg/kg were 97.43 ± 4.20, 215.01 ± 55.42, and 721.07 ± 51.81 ml/h, and apparent distribution volumes of PA in the steady state (Vz/F) at 20, 100, or 500 mg/kg were 903.28 ± 125.28, 1419.87 ± 527.53, and 5264.86 ± 993.65 ml, respectively. PA was absorbed rapidly after an oral dose of 500 mg/kg with peak concentration (Cmax) in blood (3.5 ± 0.33 µg/ml) at 30 min postadministration. After oral administration, the dose-normalized area under the curve (AUC) (146.90 ± 9.33 mg/h/ml) for 500 mg/kg was significantly greater than at 20 mg/kg (44.69 ± 2.56 mg/h/ml). Urine analysis indicated that 13 ± 0.45% of the administered PA dose (at 500 mg/kg, p.o.) was recovered unchanged in urine within 24 h.
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