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EC number: 201-622-7 | CAS number: 85-68-7
- 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
Developmental toxicity / teratogenicity
Administrative data
- Endpoint:
- developmental toxicity
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 14 December 1988 to 23 February 1989
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Acceptable, well-documented study report which meets basic scientific principles
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 989
- Report date:
- 1989
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- Deviations:
- yes
- Remarks:
- Administration of test compound only during organogenesis (days 6-15 of pregnancy) and not from pre-implantation as indicated in guideline; administration of test compound in feed rather than by gavage
- GLP compliance:
- yes
- Limit test:
- no
Test material
- Reference substance name:
- Benzyl butyl phthalate
- EC Number:
- 201-622-7
- EC Name:
- Benzyl butyl phthalate
- Cas Number:
- 85-68-7
- Molecular formula:
- C19H20O4
- IUPAC Name:
- 1-benzyl 2-butyl benzene-1,2-dicarboxylate
- Details on test material:
- - Name of test material (as cited in study report): benzyl butyl phthalate
- Substance type: no data
- Physical state: clear, oily liquid
- Analytical purity: 96%
- Impurities (identity and concentrations): 1 major and 10 minor, 3.4% in total by weight, no single impurity present at >1%; not identified
- Purity test date: no data
- Lot/batch No.: no data (RTI chemical ID = D60; RTI Log no. = 4911-40)
- Expiration date of the lot/batch: no data
- Stability under test conditions: stable throughout the period of use
- Storage condition of test material: At or below room temperature in sealed containers
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Laboratories, Inc., Raleigh, NC, USA
- Age at study initiation: 8-12 weeks
- Weight at study initiation: 250(+/-2) g
- Fasting period before study: none
- Housing: individually in solid-bottom polycarbonate cages with stainless steel wire lids and Ad-Sorb-Dri (TM) cage litter
- Diet (e.g. ad libitum): Ground Purina Certified Rodent Chow #5002 ad libitum
- Water (e.g. ad libitum): deionized/filtered water ad libitum
- Acclimation period: 7 days before cohabitation with males
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22 (average)
- Humidity (%): 48 (average)
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- oral: feed
- Vehicle:
- unchanged (no vehicle)
- Details on exposure:
- PREPARATION OF DOSED FEED: Even mixing of test chemical to required concentration
DIET PREPARATION
- Rate of preparation of diet (frequency): Once only for each dietary concentration; storage in refrigerator, with fresh supplied obtained from refrigerated stock on days 6, 9 and 12 of gestation
- Mixing appropriate amounts with (Type of food): rodent chow
- Storage temperature of food: under refrigeration - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Analysis by HPLC (high performance liquid chromatography) prior to and after use of the dosed feed verified the formulations to be within 91-108% of the theoretical concentration (0.5, 1.25 or 2%), indicating accurate preparation and stability throughout the period of use.
- Details on mating procedure:
- Impregnation procedure: cohoused
- M/F ratio per cage: 1/1
- Length of cohabitation: until detection of vaginal sperm
- Proof of pregnancy: sperm in vaginal smear referred to as day 0 of pregnancy
- Any other deviations from standard protocol: no - Duration of treatment / exposure:
- Days 6-15 of gestation (the organogenesis period)
- Frequency of treatment:
- Continuous (in feed)
- Duration of test:
- From pre-mating until gestational day 20.
Doses / concentrationsopen allclose all
- Remarks:
- Doses / Concentrations:
0, 420, 1100 or 1640 mg/kg bw/day
Basis:
other: average ingested dose
- Remarks:
- Doses / Concentrations:
0, 0.5, 1.25 or 2%
Basis:
nominal in diet
- No. of animals per sex per dose:
- 30 pregnant females/dose
- Control animals:
- yes, plain diet
- Details on study design:
- - Dose selection rationale: Preliminary study at dietary concentrations of 0, 0.25, 0.5, 1, 2.5 and 5% (in 5-8 confirmed-pregnant females per dose group) indicated no maternal or embryo/foetal toxicity at less than or equal to 1%, but excessive maternal and embryo/foetal toxicity at 2.5%.
- Rationale for animal assignment (if not random): stratified randomization so that body weights did not differ among groups
Examinations
- Maternal examinations:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: daily
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: daily
BODY WEIGHT: Yes
- Time schedule for examinations: every 3 days from gestational day 0; final examination after sacrifice
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study): Yes - calculated every 3 days from gestational day 0; final calculation before sacrifice
- Food consumption for each animal determined and mean daily diet consumption calculated as g food/kg body weight/day: Yes
- Compound intake calculated as time-weighted averages from the consumption and body weight gain data: Yes
POST-MORTEM EXAMINATIONS: Yes
- Sacrifice on gestation day #20
- Organs examined: liver (weighed and a random selection from control and high-dose groups were examined microscopically), kidneys (weighed), uterus (weighed intact)
OTHER: water intake calculated every 3 days from gestational day 0; final calculation before sacrifice; pregnancy rate recorded for each group - Ovaries and uterine content:
- The ovaries and uterine content was examined after termination: Yes
Examinations included:
- Gravid uterus weight: Yes
- Number of corpora lutea: Yes
- Number of implantations: Yes
- Number of early resorptions: Yes
- Number of late resorptions: Yes - Fetal examinations:
- - External examinations: Yes: all per litter
- Soft tissue examinations: Yes: all per litter
- Skeletal examinations: Yes: all per litter
- Head examinations: Yes: half per litter - Statistics:
- - General Linear Models (GLM) were applied for the analyses of variance (ANOVA) of maternal and foetal parameters; prior arcsine-square root transformation on all litter-derived percentage data and Bartlett's test for homogeneity of variance on all data to be analysed by ANOVA
- When ANOVA revealed a significant dose-effect, Williams' and Dunnett's Multiple Comparison tests were used to compare exposed to control groups
- One-tailed tests were used for pairwise comparisons (except maternal body and organ weights and foetal body weights)
- X2 test for independence, "a test" for linear trend on proportions and Fisher's exact probability test were used on some data - Historical control data:
- Included in appendices to report. No major differences, where comparable, between these and control data from present study.
Results and discussion
Results: maternal animals
Maternal developmental toxicity
- Details on maternal toxic effects:
- Maternal toxic effects:yes
Details on maternal toxic effects:
At 1.25% in the diet there was a 37% reduction in weight gain (during treatment), an increase in relative liver weight, and increases in relative food and water intakes. At 2% in the diet, decreased maternal weight gain persisted throughout the remainder of the gestation period (93% decrease) and increased food and water intakes were more pronounced; liver weight changes were also more pronounced (although there were no microscopic changes). Relative kidney weights were increased and there were clinical signs of toxicity including hair loss, piloerection, coat discolouration, lethargy, excessive urination, muscular weakness and abnormal gait.
Effect levels (maternal animals)
open allclose all
- Dose descriptor:
- NOAEL
- Effect level:
- ca. 420 mg/kg bw/day (nominal)
- Basis for effect level:
- other: maternal toxicity
- Dose descriptor:
- NOAEL
- Effect level:
- ca. 420 mg/kg bw/day (nominal)
- Basis for effect level:
- other: developmental toxicity
Results (fetuses)
- Details on embryotoxic / teratogenic effects:
- Embryotoxic / teratogenic effects:yes
Details on embryotoxic / teratogenic effects:
At 1.25% in the diet there was a slight increase in the percentage of foetuses/litter with external, visceral and skeletal malformations (5.9 +/- 1.6, compared with 2.0 +/- 0.8 in the controls); at 2% in the diet the percentage (52.8 +/- 6.6) was statistically significantly increased. The urogenital system, eye, heart and axial skeleton were the most frequently affected. The high-dose group also showed increased resorptions (with a 33% reduction in liver foetuses per litter) and a 20% reduction in foetal body weights.
Fetal abnormalities
- Abnormalities:
- not specified
Overall developmental toxicity
- Developmental effects observed:
- not specified
Applicant's summary and conclusion
- Conclusions:
- Benzyl butyl phthalate given to pregnant rats in the diet at levels of 0.5, 1.25 or 2% (resulting in intakes of 0, 420, 1100 or 1640 mg/kg bw/day respectively), on days 6-15 of pregnancy, was found to cause developmental and maternal toxicity at the two higher dose levels. There were no apparent effects on mothers or their foetuses at the lowest tested dose of 0.5%, which was considered to be the no-observed-adverse-effect level (NOAEL) for both maternal and developmental endpoints.
- Executive summary:
A well-conducted study was performed in rats to assess the potential of benzyl butyl phthalate to cause developmental toxicity.
Using a similar protocol to that outlined by OECD Test Guideline 414, groups of 30 pregnant rats were given diets containing 0, 0.5, 1.25 or 2% benzyl butyl phthalate (providing 0, 420, 1100 or 1640 mg/kg bw/day respectively) on days 6 -15 of pregnancy. Maternal weight gain, clinical signs and food and water intakes were monitored, and the dams were killed on day 20 of pregnancy. The uterus, liver and kidney were weighed, and some livers from the high-dose and control groups were examined microscopically. The uterine contents were examined for implantations and resorptions. Viable foetuses were weighed and evaluated for external, soft tissue and skeletal malformations.
At 1.25% in the diet, the mothers showed reduced weight gain during treatment, increased relative liver weight and increased relative food and water intakes. At this dose there was a slight (but not statistically significant) increase in the numbers of litters with external, visceral and skeletal malformations.
At 2% in the diet, the maternal effects described above were more pronounced and accompanied by increased kidney weights; there were also clinical signs of toxicity including hair loss, piloerection, coat discolouration, lethargy, excessive urination, muscular weakness and abnormal gait. Foetal malformations were statistically significantly increased (53% malformed foetuses per litter compared to 2% in controls), with the urogenital system, eye, heart and axial skeleton most frequently affected. Increased resorptions and reduced foetal body weights were also reported.
In conclusion, the NOAEL for both maternal and foetal effects was 0.5% (420 mg/kg bw/day).
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