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EC number: 940-786-0 | CAS number: -
- 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
Two key studies for read-across source substances of Benzene, C15-16-alkyl derivs. have been conducted that provide information on repeated dose toxicity. At very high daily dietary doses to the test substance, rats exhibited reduced food consumption and body weight gains beginning at the lowest dose of 2500 ppm . No other effects or abnormalities were observed. In rats exposed to daily oral gavage doses ranging from 5 to 500 mg/kg bw/day of LAB through two generations, no adverse effects were observed except for reductions in body weight gain at the highest dose. Therefore it is clear that the primary effect of the test substance at high daily doses is reduced body weight gain, probably as a function of the poor palatability of the test substance.
Key value for chemical safety assessment
Repeated dose toxicity: via oral route - systemic effects
Link to relevant study records
- Endpoint:
- sub-chronic toxicity: oral
- Type of information:
- migrated information: read-across based on grouping of substances (category approach)
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: GLP study published in peer-reviewed journal.
- Qualifier:
- according to guideline
- Guideline:
- other: OECD 416 2-generation reproductive study
- GLP compliance:
- yes
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Breeding Laboratories
- Housing: wire mesh cages
- Diet (e.g. ad libitum): Ralson Purina commercial laboratory feed, ad libitum
- Water (e.g. ad libitum): tap water, ad libitum
ENVIRONMENTAL CONDITIONS
- Temperature (°F): 65-79
- Humidity (%): 17-76
- Photoperiod (hrs dark / hrs light): 12 hrs light/12 hrs dark - Route of administration:
- oral: gavage
- Vehicle:
- corn oil
- Duration of treatment / exposure:
- daily
- Frequency of treatment:
- F0: Treatment was started 10 weeks before mating. For males, dosing continued for 2 weeks after mating (total of 105 days). For females, dosing continued through lactation for a total of 127 treatment days.
- Remarks:
- Doses / Concentrations:
0, 5, 50 and 500 mg/kg
Basis:
actual ingested - No. of animals per sex per dose:
- 30 animals of each sex per dose
- Control animals:
- yes, concurrent vehicle
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: twice daily
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: weekly
BODY WEIGHT: Yes
- Time schedule for examinations: males - weekly, females - weekly before mating, days 0, 7, 14, and 20 of gestation, and days 0, 4, 14, and 21 of lactation
FOOD CONSUMPTION: weekly - Sacrifice and pathology:
- SACRIFICE
- Male animals: All surviving animals 2 weeks after mating.
- Maternal animals: All surviving animals at weaning.
GROSS NECROPSY
- Gross necropsy consisted of examination for gross lesions
HISTOPATHOLOGY / ORGAN WEIGHTS
pituitary glands, testes and epididymides, prostate and seminal vesicles, vagina, uterus, ovaries, and gross lesions - Clinical signs:
- no effects observed
- Mortality:
- no mortality observed
- Body weight and weight changes:
- effects observed, treatment-related
- Food consumption and compound intake (if feeding study):
- no effects observed
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- not examined
- Clinical biochemistry findings:
- not examined
- Urinalysis findings:
- not examined
- Behaviour (functional findings):
- not examined
- Organ weight findings including organ / body weight ratios:
- not examined
- Gross pathological findings:
- no effects observed
- Histopathological findings: non-neoplastic:
- no effects observed
- Histopathological findings: neoplastic:
- no effects observed
- Details on results:
- CLINICAL SIGNS AND MORTALITY (PARENTAL ANIMALS)
No mortality attributed to treatment was observed.
BODY WEIGHT AND FOOD CONSUMPTION
Mean body weights of high-dose-group (500 mg/kg bw/d) males were significantly and consistently reduced {12 = 0.01) in the FO (since premating week); mean body weights of high-dose females were significantly decreased in the FO generation since the 9th week of premating until the first week of lactation (p = 0.05); body weight reduction was significant on day 20 of gestation in both generations (p = 0.01
GROSS PATHOLOGY (PARENTAL ANIMALS)
No gross postmortem findings.
HISTOPATHOLOGY (PARENTAL ANIMALS)
No histopathological findings.
- Dose descriptor:
- NOAEL
- Effect level:
- 50 mg/kg bw (total dose)
- Sex:
- male/female
- Basis for effect level:
- other: reduced weight gain in the high dose group
- Dose descriptor:
- LOAEL
- Effect level:
- 500 mg/kg bw (total dose)
- Sex:
- male/female
- Basis for effect level:
- other: reduced weight gain
- Critical effects observed:
- not specified
- Conclusions:
- The NOAEL was 50 mg/kg bw/day in both male and female rats.
- Executive summary:
In cases where no data were available on the target substance, Benzene, C15 -16 -alkyl derivs., data were read across from a structurally related material (the test substance).
This study examined the effects of repeated exposure to the test substance. Groups of 30 female and 30 male rats were exposed to concentrations of 0, 5, 50 and 500 mg/kg day of test substance by oral gavage beginning ten weeks before mating. Animals were then mated. The resulting generation was also exposed to the test substance and mated. Exposure continued through the mating period, and in females through the gestation and lactational periods. Males were exposed for a total of 105 days, and females 127 days. All animals were sacrificed and necropsied after exposure. During the study, animals were observed for clinical signs, mortality, and body weight. The NOAEL was 50 mg/kg/day and the LOAEL was 500 mg/kg/day based on reduced weight gain in the high dose group.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 50 mg/kg bw/day
- Study duration:
- subacute
- Species:
- rat
Repeated dose toxicity: inhalation - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: inhalation - local effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - local effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Additional information
In cases where no data were available on the target substance, Benzene, C15-16-alkyl derivs., data were read across from a structurally related material (the test substance).
Two key studies for read-across source substances of Benzene, C15 -16 -alkyl derivs. have been conducted that provide information on the repeated dose toxicity of LAB. At very high daily dietary doses to LAB, rats exhibited reduced food consumption and body weight gains beginning at the lowest dose of 2500 ppm . No other effects or abnormalities were observed. In rats exposed to daily oral gavage doses ranging from 5 to 500 mg/kg bw/day of LAB through two generations, no adverse effects were observed except for reductions in body weight gain at the highest dose. Therefore it is clear that the primary effect of LAB at high daily doses is reduced body weight gain, probably as a function of the poor palatability of the test substance.
Two key studies are available to document the potential effects from repeated exposures to a read-across source substance for Benzene, C15 -16 -alkyl derivs. The first key study (Monsanto 1997) examined the effects of dietary exposure of rats to the test substance. Groups of rats were given daily diets containing 0, 2500, 5000, 7500, or 20000 ppm test substance (corresponding to 0, 125, 250, 375, 1000 mg/kg bw/day) for 28 days. Animals were observed for food consumption and body weight changes. At the end of the study, the animals were sacrificed and examined for gross pathology. Histopathology was not carried out. Reduced food consumption and body weight gain was noted at all dose levels. No abnormalities were seen in the gross pathology examinations. Since there were effects at the lowest dose tested (2500 ppm, which corresponds to 125 mg/kg bw), the LOAEL was 125 mg/kg/day (NOAEL <125 mg/kd/day).
In the second key study (Robinson and Schroeder 1992), groups of 30 female and 30 male rats were exposed to concentrations of 0, 5, 50 and 500 mg/kg bw/day of test substance by oral gavage beginning ten weeks before mating. Animals were then mated and the resulting generation was also exposed to the test substance and mated. Exposure continued through the mating period, and in females through the gestation and lactational periods. Males were exposed for a total of 105 days, and females 127 days. All animals were sacrificed and necropsied after exposure. During the study, animals were observed for clinical signs, mortality, and body weight. No effects were observed in mortality, clinical signs, food consumption, histopathology, or other parameters, with the exception of body weight gain. Mean body weights of males in the high dose group (500 mg/kg bw/d) were significant and consistently reduced in F0 group (since premating week). Mean body weights of high dose females were significantly decreased in the F0 generation beginning in the 9th week of premating until the first week of lactation. Body weight reduction was significant on day 20 of gestation in both generations. Therefore, the NOAEL was 50 mg/kg/day and the LOAEL was 500 mg/kg/day based on reduced weight gain in the high dose group.
Justification for classification or non-classification
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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