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EC number: 800-838-4 | CAS number: 1384855-91-7
- 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
Endpoint summary
Administrative data
Description of key information
Based on the study results, the acute oral LD50 of the test substance was determined to be >2000 mg/kg bw.
Based on the results of read across study, the acute dermal LD50 of the test substance is considered to be >2000 mg/kg bw.
Key value for chemical safety assessment
Acute toxicity: via oral route
Link to relevant study records
- Endpoint:
- acute toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- From 6 April, 2012 to 26 April, 2012
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 423 (Acute Oral toxicity - Acute Toxic Class Method)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.1 tris (Acute Oral Toxicity - Acute Toxic Class Method)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 870.1100 (Acute Oral Toxicity)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- other: Japanese Ministry of Agriculture, Forestry and Fisheries (JMAFF), 12 Nohsan, Notification No 8147, April 2011, including the most recent partial revisions.
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Test type:
- acute toxic class method
- Limit test:
- no
- Species:
- rat
- Strain:
- other: Wistar strain, Crl:WI (Han)
- Sex:
- female
- Details on test animals or test system and environmental conditions:
- - Source: Charles River Deutschland, Sulzfeld, Germany.
- Age at study initiation: Young adult animals (approx. 8-9 weeks old)
- Weight at study initiation: Body weight variation was within +/- 20% of the sex mean (first group: 156 - 178 g; second group: 149 - 157 g).
- Fasting period before study: Animals were deprived of food overnight prior to dosing and until 3-4 h after administration of the test substance. Water was available ad libitum.
- Housing: Group housing of 3 animals per cage in labeled Macrolon cages
- Diet: Free access to pelleted rodent diet (SM R/M-Z from SSNIFF® Spezialdiäten GmbH, Soest, Germany).
- Water: Free access to tap water.
- Acclimation period: At least 5 d
ENVIRONMENTAL CONDITIONS
Environmental controls for the animal room were set to maintain 18 to 24°C, a relative humidity of 40 to 70%, approx 15 room air changes/h, and a 12-h light/12-h dark cycle.
IN-LIFE DATES: From 06 April 2012 to 26 April 2012 - Route of administration:
- oral: gavage
- Details on oral exposure:
- GAVAGE METHOD: Plastic feeding tubes.
Frequency: Single dosage, on Day 1.
VEHICLE Polyethylene glycol 400 (Merck, Darmstadt, Germany) (specific gravity 1.125).
- Justification for choice of vehicle: The vehicle was selected based on trial formulations performed at NOTOX and on test substance data supplied by the sponsor.
MAXIMUM DOSE VOLUME APPLIED: 2000 mg/kg (10 mL/kg) bw.
DOSAGE PREPARATION:
The formulations (w/w) were prepared using amber coloured glassware within 4 h prior to dosing. Homogeneity was accomplished to a visually acceptable level. Adjustment was made for specific gravity of the test substance and vehicle. No correction was made for purity of the test substance. - Doses:
- 2000 mg/kg bw
- No. of animals per sex per dose:
- 6 (2 groups of three females in a stepwise manner)
- Control animals:
- no
- Details on study design:
- - Duration of observation period following administration: 14 d
- Frequency of observations and weighing:
Mortality/Viability: Twice daily
Body weights: Days 1 (pre-administration), 8 and 15.
Clinical signs: At periodic intervals on the day of dosing (Day 1) and once daily thereafter, until Day 15.
- Necropsy of survivors performed: At the end of the observation period, all animals were sacrificed by oxygen/carbon dioxide procedure and subjected to necropsy. Descriptions of all internal macroscopic abnormalities were recorded.
- Other examinations performed: none. - Statistics:
- No statistical analysis was performed (The method used is not intended to allow the calculation of a precise LD50 value).
- Key result
- Sex:
- female
- Dose descriptor:
- LD50
- Effect level:
- > 2 000 mg/kg bw
- Based on:
- test mat.
- Mortality:
- No mortality occurred.
- Clinical signs:
- other: Hunched posture and/or piloerection was noted in all animals on Day 1.
- Gross pathology:
- No abnormalities were found at macroscopic post mortem examination of the animals.
- Interpretation of results:
- other: EU CLP criteria not met
- Conclusions:
- Under the study conditions, the oral LD50 value of the test substance in rats was considered to be > 2,000 mg/kg bw.
- Executive summary:
A study was conducted to determine the acute oral toxicity of test substance, DPHA according to OECD Guideline 423, EU method B.1 tris, EPA OPPTS 870.1100 and Japanese Ministry of Agriculture, Forestry and Fisheries (JMAFF) Guidelines, in compliance with GLP. The test substance was administered by oral gavage to two groups of three female Wistar rats at 2,000 mg/kg bw. No mortality occurred. Hunched posture and/or piloerection were noted in all animals on Day 1. The body weight gain shown over the study period was similar to that expected of normal untreated animals of the same age and strain. No abnormalities were found at macroscopic post-mortem examination. Under the study conditions, the oral LD50 value of the test substance in rats was considered to be > 2,000 mg/kg bw (Beerens-Heijnen, 2012).
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 2 000 mg/kg bw
- Quality of whole database:
- The information requirements for this tonnage band is sufficiently met with the available data.
Acute toxicity: via inhalation route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Acute toxicity: via dermal route
Link to relevant study records
- Endpoint:
- acute toxicity: dermal
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- From 14 Oct, 1980 to 28 Oct, 1980
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Remarks:
- KL2 due to RA
- Justification for type of information:
- Refer to section 13 of IUCLID for details on the read-across justification.
- Reason / purpose for cross-reference:
- read-across source
- Qualifier:
- according to guideline
- Guideline:
- other: 40 CFR Part 163.81-2 (Environmental Protection Agency, Pesticides Programs, Proposed Guidelines for Registering Pesticides in the U.S.; Hazard Evaluation: Humans and Domestic Animals. Acute Dermal Toxicity)
- Deviations:
- no
- GLP compliance:
- not specified
- Limit test:
- yes
- Species:
- other: Albino rabbits
- Strain:
- New Zealand White
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Penn Dutch Laboratory animals, Denver, Pennsylvania
- Age at study initiation: Young adults
- Weight at study initiation: 2.2 to 2.8 kg (males), 2.5 to 2.9 kg (females)
- Housing: Individually housed
- Diet: Purina Rabbit Chow, ad libitum
- Water: Automatic watering system, ad libitum.Municipal water supply (Elizabethtown Water Co. )
ENVIRONMENTAL CONDITIONS
- Temperature: 60 to 66°F
- Photoperiod: 12 h light, 12 h dark - Type of coverage:
- occlusive
- Vehicle:
- unchanged (no vehicle)
- Details on dermal exposure:
- On the day before dosing (approx 18 h prior to dosing), the hair of each rabbit was closely clipped from the trunk with an electric clipper, so as to expose at least 10% of the body surface area. Just prior to dosing, the skin of all of the animals was abraded longitudinally every 2 or 3 cm over the area of exposure, deep enough to penetrate the stratum corneum, but not so deep as to disturb the dermis or produce bleeding. The test substance was applied directly onto the exposed skin of the animal, and spread evenly over the entire area. A layer of 8-ply gauze was then wrapped around the animal to cover the application site. The animal was then wrapped in an impervious plastic sleeve, designed to contain the test substance without leakage or undue pressure. The sleeve was secured with masking tape and Elizabethan collars were placed on all animals. Following approx 24 h of exposure, the wrappings were removed and the test site wiped free of excess test substance. After 30 min, dermal observations were made.
- Duration of exposure:
- 24 h
- Doses:
- 2000 mg/kg bw
- No. of animals per sex per dose:
- 10 (six males, four females)
- Control animals:
- not required
- Details on study design:
- - Duration of observation period following administration: 14 d
- Frequency of observations and weighing: Approx 1, 2, and 4 h after dosing and daily thereafter for 14 d.
- Necropsy of survivors performed: Gross post mortem examinations were performed on all animals which died or were found dead during the study. All animals surviving at termination of the observation period (Day 14) were killed by an intravenous overdose of sodium pentobarbital and examined grossly. All abnormalities were recorded hut no tissues were saved.
- Other examinations performed: Clinical signs, body weight - Key result
- Sex:
- male/female
- Dose descriptor:
- LD50
- Effect level:
- > 2 000 mg/kg bw
- Based on:
- test mat.
- Mortality:
- No
- Clinical signs:
- other: No
- Other findings:
- All animals exhibited well-defined to severe erythema with moderate or severe edema at 24 h. Two animals exhihited eschar at the dosing site
at terminal necropsy. Several animals exhibited nasal and/or oral or ocular discharge during the 14 d post-dose period. A single animal exhibited decreased food consumption and fecal staining of the abdomen at 24 h only. - Interpretation of results:
- other: EU CLP criteria not met
- Conclusions:
- Under the study conditions, the dermal LD50 of the test substance was determined to be >2,000 mg/kg bw in rabbits.
- Executive summary:
A study was conducted to determine the acute dermal toxicity of the read-across substance, PETIA in rabbits according to the EPA 40 CFR Part 163.81-2. A single dose of 2,000 mg/kg bw was administered at a dose volume of 1.7 mL/kg bw to ten rabbits (six males and four females). Following approximately 24 h of exposure, the wrappings were removed and the test site wiped free of excess test substance. After 30 min, dermal observations were made. No mortality occurred and most animals gained weight in the 14 d period after dosing although one male and one female exhibited weight loss. All animals showed well-defined to severe erythema with moderate or severe edema at 24 h. In two animals, eschar was seen at the dosing site at terminal necropsy. Several animals had nasal and/or oral or ocular discharge during the 14 d post-dose period. A single animal exhibited decreased food consumption and fecal staining of the abdomen at 24 h only. Under the study conditions, the dermal LD50 of the test substance was determined to be >2,000 mg/kg bw in rabbits (Auletta, 1980).
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 2 000 mg/kg bw
- Quality of whole database:
- The information requirements for this tonnage band is sufficiently met with the available data.
Additional information
Oral
A study was conducted to determine the acute oral toxicity of test substance, DPHA according to OECD Guideline 423, EU method B.1 tris, EPA OPPTS 870.1100 and Japanese Ministry of Agriculture, Forestry and Fisheries (JMAFF) Guidelines, in compliance with GLP.The test substance was administered by oral gavage to two groups of three female Wistar rats at 2000 mg/kg bw. No mortality occurred. Hunched posture and/or piloerection were noted in all animals on Day 1. The body weight gain shown over the study period was similar to that expected of normal untreated animals of the same age and strain. No abnormalities were found at macroscopic post-mortem examination. Under the study conditions, the oral LD50 value of the test substance in rats was considered to be > 2000 mg/kg bw (Beerens-Heijnen, 2012).
Dermal
A study was conducted to determine the acute dermal toxicity of the read-across substance, PETIA in rabbits according to the EPA 40 CFR Part 163.81-2.A single dose of 2000 mg/kg bw was administered at a dose volume of 1.7 mL/kg bw to ten rabbits (six males and four females). Following approximately 24 h of exposure, the wrappings were removed and the test site wiped free of excess test substance. After 30 min, dermal observations were made. No mortality occurred and most animals gained weight in the 14 d period after dosing although one male and one female exhibited weight loss. All animals showed well-defined to severe erythema with moderate or severe edema at 24 h. In two animals, eschar was seen at the dosing site at terminal necropsy. Several animals had nasal and/or oral or ocular discharge during the 14 d post-dose period. A single animal exhibited decreased food consumption and fecal staining of the abdomen at 24 h only.Under the study conditions, the dermal LD50 of the test substance was determined to be >2000 mg/kg bw in rabbits (Auletta, 1980).
Justification for classification or non-classification
The available data for DPHA and the read-across substance PETIA indicates a low potential for acute oral (LD50 > 2000 mg/kg bw) and dermal (LD50 > 2000 mg/kg bw) toxicity. The substance therefore does not meet the requirement for classification according to EU CLP (EC 1272/2008) criteria.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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