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EC number: 249-951-5 | CAS number: 29911-28-2
- 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:
- July 1987- June 1988
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP-study according to OECD guideline 414
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 988
- Report date:
- 1988
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- Principles of method if other than guideline:
- n/a
- GLP compliance:
- yes
- Limit test:
- no
Test material
- Reference substance name:
- 1-(2-butoxy-1-methylethoxy)propan-2-ol
- EC Number:
- 249-951-5
- EC Name:
- 1-(2-butoxy-1-methylethoxy)propan-2-ol
- Cas Number:
- 29911-28-2
- Molecular formula:
- C10H22O3
- IUPAC Name:
- 1-(2-butoxy-1-methylethoxy)propan-2-ol
- Details on test material:
- Identity: Dowanol-DPnB (n-butoxypropoxypropanol or
dipropylene glycol normal-butyl ether).
CAS # 29911-28-2.
Appearance: Clear, colorless liquid.
Batch No.: XZ451100.
Source: Dow Chemical Europe, Horgen, Switzerland.
Expiration Date: None specified.
Purity: >95%.
Specific Gravity: 0.91 kg/liter.
Solubility in
water: 5%.
Stability: Stable up to 200°C.
Storage: Ambient temperature in dark.
Administered as: Dilution in 1% Methocel and water.
Constituent 1
Test animals
- Species:
- rat
- Strain:
- other: Wistar derived SPF-bred albino rats (Bor; WISW, SPF TNO)
- Details on test animals or test system and environmental conditions:
- Age at dosing: Approximately 12 weeks (females) and 13 eeks (males) of age.
Source: Winkelmann Versuchstierzucht GmbH & Co. KG, Borchen, West-Germany.
Acclimation period: Approximately 1 week.
Average weight (start of study): Males: not specified Females: 186 - 209 grams.
Assignment to groups: Computerized, random number-based procedure.
Diet: "Basal Diet" (analysis provided in report)
Access to food: Available ad libitum.
Access to water: Available ad libitum.
Method of Identification: "V" notches on ears.
Housing: Prior to mating: males - individually, females - 5 per group in stainless steel cages with wire-mesh bottoms.
After mating: housing-type for females not specified.
Environmental Conditions:
Temperature: 22 ± 2°C. Recording frequency not reported.
Humidity: At least 40%. Range & recording frequency not reported.
Air changes: 8-10 air changes per hour.
Photoperiod: 12 hr light/12 hr dark.
Administration / exposure
- Route of administration:
- dermal
- Type of inhalation exposure (if applicable):
- not specified
- Vehicle:
- propylene glycol
- Details on exposure:
- Dipropylene glycol n-butyl ether (DPnB) was applied daily to the skin of pregnant rats on gestation days 6 through 15 (detection of sperm in vaginal smears was designated day 0). DPnB was applied to the clipped skin of two groups of Wistar rats (>20/sex/dose level) at various dilutions in propylene glycol (PG) equivalent to doses of 0 (PG-only; 1.5 ml/kg-day), 0.3 or 1.0 ml DPnB/kg-day. These doses equate to 0, 273, or 910 mg DPnB/kg-day. Treatment solutions were applied to the clipped dorsal trunk of each rat over an area of about 20 cm2. Dilutions of DPnB in PG resulted in applied volumes of 1.5 ml (PG-only), 1.8 ml (1.5 ml PG & 0.3 ml DPnB), or 2.5 ml (1.5 ml PG & 1.0 ml DPnB) test solution per kg body weight. Rats wore neck collars to prevent grooming and ingestion of test material. Solutions were applied unoccluded since the low vapor pressure of DPnB and PG precluded evaporative loss.
- Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- The content of DPnB was determined in the test solutions prepared on July 20-1987. Samples were taken from each solution and stored at -20 celcius until further analysis. The analysis was carried out at TNO Institute CIVO-Analysis.
- Details on mating procedure:
- Females were placed overnight with males, e.g. two females with one male. Vaginal smears were taken to determine whether mating occured. If no sperm cells were detected, the female of question was placed with another male again. The day of detection of sperm cells was considered day 0 of pregnancy. This procedure was continued for 4 days to have sufficient number of possibly pregnant animals in each of the groups. Animals found to have mated were assigned to each group in rotation.
- Duration of treatment / exposure:
- Days 6-15 of gestation (day plug found was Day 0)
- Frequency of treatment:
- daily
- Duration of test:
- Treatment from Day 0 to Day 15 of pregnancy. Test until day 21 of pregnancy.
- No. of animals per sex per dose:
- 22 in control, 21 in 273 mg/kg, and 25 in 910 mg/kg dose group.
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- Sex: female
Duration of test: until day 21 of pregnancy
Examinations
- Maternal examinations:
- Rats were observed for clinical signs of toxicity and skin reactions on a daily basis (week days). Individual body weights were recorded on days 0, 6, 16, and 21 of pregnancy and food consumption was monitored over days 0 - 6, 6 - 16, and 16 - 21 of pregnancy. At sacrifice, all animals were subjected to necropsy and examined for gross abnormalities.
- Ovaries and uterine content:
- The number of corpora lutea was counted.
- Fetal examinations:
- Fetuses were removed from the uterus, weighed, lengths recorded, and examined for gross abnormalities. Early and late resorptions and live and dead fetuses were counted. Implantation sites in both uterine horns were counted and the empty uterus weighed. Half the fetuses from each litter were eviscerated, skinned and stripped of most subcutaneous tissue, then fixed in 96% ethanol. These fetuses were then stained with Alizarin Red S for examination for skeletal anomalies. The remaining fetuses were fixed in Bouin's fluid, transferred to 70% ethanol and sectioned into slices (after Wilson) for soft tissue examination. Percentages of pre- and post-implantation loss were calculated, as was the degree of ossification for each fetus. Soft tissue and skeletal anomalies or abnormalities were recorded.
- Statistics:
- For the statistical analysis of difference in degree of ossification between test and control student t-test was applied. Statistical analysis for the body weight, food consumption, organ weights, litter data, foetus weights and lengths, and placenta weights was carried out by applying analysis of (co)-variance, with body weight on day 0 as covairable, followed by Dunnet's multiple comparison test, whereas skeletal and visceral anormalies were evaluated by the Chi-square test.
- Indices:
- Percentage pre-implantation loss (PRIL)
Percentage post-implantation loss (POIL)
Degree of ossificatin of foetus skeleton (DgO)
Transformed ossification values (DfOt) - Historical control data:
- Incidence of spontaneous malformations, anomalies and variants in Albino rats of the Wistar strain (Cpb-WU; Wistar random). TNO report # v82.043/020283
Results and discussion
Results: maternal animals
Maternal developmental toxicity
- Details on maternal toxic effects:
- Maternal toxic effects:no effects
Details on maternal toxic effects:
Slight skin reactions were found in the dams from all treatment groups and thus were not considered to be treatment related. No maternal toxicity was found: clinical signs and organ or body weights did not differ between treatment and controls groups. No deaths occurred in any groups over the course of the study. Fecundity was comparable among groups.
Effect levels (maternal animals)
- Dose descriptor:
- NOAEL
- Effect level:
- 910 mg/kg bw/day
- Basis for effect level:
- other: maternal toxicity
Results (fetuses)
- Details on embryotoxic / teratogenic effects:
- Embryotoxic / teratogenic effects:no effects
Details on embryotoxic / teratogenic effects:
No embryo- or fetotoxicity was evident since pre- and post-implantation loss, number of viable fetuses, and fetal weights and lengths were comparable between treatment and control groups. DPnB did not cause frank developmental toxicity in skeletal or soft tissue. Frank skeletal malformations were observed only in the control group (6 fetuses from 2 litters). Skeletal variants were observed in all dose groups. The high dose group did exhibit a slight increase (not statistically significant) in the incidence of supernumerary rudimentary thoracic ribs when compared to controls. However, this finding was not considered biologically significant by the authors of the study since the incidence was within normal limits for these species.
Effect levels (fetuses)
- Dose descriptor:
- NOAEL
- Effect level:
- 910 mg/kg bw/day
- Sex:
- male/female
- Basis for effect level:
- other: teratogenicity
Fetal abnormalities
- Abnormalities:
- not specified
Overall developmental toxicity
- Developmental effects observed:
- not specified
Applicant's summary and conclusion
- Conclusions:
- DPnB is not maternally toxic, embryo- or fetotoxic, or teratogenic in Wistar rats receiving dermal doses up to 1.0 ml/kg-d during organogenesis (days 6 - 15). The NOAEL for maternal toxicity, embryo- or fetal toxicity, or developmental toxicity is 1.0 ml/kg-d (910 mg/kg-d) and a LOAEL was not established.
- Executive summary:
Dipropylene glycol n-butyl ether (DPnB) was applied daily to the skin of pregnant rats on gestation days 6 through 15 (detection of sperm in vaginal smears was designated day 0). DPnB was applied to the clipped skin of two groups of Wistar rats (>20/sex/dose level) at various dilutions in propylene glycol (PG) equivalent to doses of 0 (PG-only; 1.5 ml/kg-day), 0.3 or 1.0 ml DPnB/kg-day. These doses equate to 0, 273, or 910 mg DPnB/kg-day. Treatment solutions were applied to the clipped dorsal trunk of each rat over an area of about 20 cm2. Dilutions of DPnB in PG resulted in applied volumes of 1.5 ml (PG-only), 1.8 ml (1.5 ml PG & 0.3 ml DPnB), or 2.5 ml (1.5 ml PG & 1.0 ml DPnB) test solution per kg body weight. Rats wore neck collars to prevent grooming and ingestion of test material. Solutions were applied unoccluded since the low vapor pressure of DPnB and PG precluded evaporative loss.
The content of DPnB was determined in the test solutions prepared on July 20-1987. Samples were taken from each solution and stored at -20 celcius until further analysis. The analysis was carried out at TNO Institute CIVO-Analysis.
Females were placed overnight with males, e.g. two females with one male. Vaginal smears were taken to determine whether mating occured. If no sperm cells were detected, the female of question was placed with another male again. The day of detection of sperm cells was considered day 0 of pregnancy. This procedure was continued for 4 days to have sufficient number of possibly pregnant animals in each of the groups. Animals found to have mated were assigned to each group in rotation.
Pregnant animals were randomly assigned to each groups, with 22 in control, 21 in 273 mg/kg, and 25 in 910 mg/kg dose group. Treatments of the animals were conducted on days 6-15 of gestation (day plug found was Day 0) daily. The doses used were 273 or 910 mg/kg.
The experimental design is shown in the table below.
Group DPnB Vehicle DPnB No/F Treatment
Dose PG Dose Dose Dose Period
(ml/kg-d) (ml/kg-d) (mg/kg-d) Group (days)
===========================================================
1 0 1.5 0 22 6 thru 15 gest.
2 0.3 1.5 273 21 6 thru 15 gest.
3 1.0 1.5 910 25 6 thru 15 gest.Rats were observed for clinical signs of toxicity and skin reactions on a daily basis (week days). Individual body weights were recorded on days 0, 6, 16, and 21 of pregnancy and food consumption was monitored over days 0 - 6, 6 - 16, and 16 - 21 of pregnancy. At sacrifice, all animals were subjected to necropsy and examined for gross abnormalities. The number of corpora lutea was counted. Fetuses were removed from the uterus, weighed, lengths recorded, and examined for gross abnormalities. Early and late resorptions and live and dead fetuses were counted. Implantation sites in both uterine horns were counted and the empty uterus weighed. Half the fetuses from each litter were eviscerated, skinned and stripped of most subcutaneous tissue, then fixed in 96% ethanol. These fetuses were then stained with Alizarin Red S for examination for skeletal anomalies. The remaining fetuses were fixed in Bouin's fluid, transferred to 70% ethanol and sectioned into slices (after ) for soft tissue examination. Percentages of pre- and post-implantation loss were calculated, as was the degree of ossification for each fetus. Soft tissue and skeletal anomalies or abnormalities were recorded. For the statistical analysis of difference in degree of ossification between test and control student t-test was applied. Statistical analysis for the body weight, food consumption, organ weights, litter data, foetus weights and lengths, and placenta weights was carried out by applying analysis of (co)-variance, with body weight on day 0 as covairable, follwoed by Dunnet's multiple comparison test, whereas skeletal and visceral anormalies were evaluated by the Chi-square test.
Indeces include Percentage pre-implantation loss (PRIL), Percentage post-implantation loss (POIL), Degree of ossificatin of foetus skeleton (DgO) and Transformed ossification values (DfOt). Incidence of spontaneous malformations, anomalies and variants in Albino rats of the Wistar strain (Cpb-WU; Wistar random). TNO report # v82.043/020283.
Slight skin reactions were found in the dams from all treatment groups and thus were not considered to be treatment related. No maternal toxicity was found: clinical signs and organ or body weights did not differ between treatment and controls groups. No deaths occurred in any groups over the course of the study. Fecundity was comparable among groups. No embryo- or fetotoxicity was evident since pre- and post-implantation loss, number of viable fetuses, and fetal weights and lengths were comparable between treatment and control groups. DPnB did not cause frank developmental toxicity in skeletal or soft tissue. Frank skeletal malformations were observed only in the control group (6 fetuses from 2 litters). Skeletal variants were observed in all dose groups. The high dose group did exhibit a slight increase (not statistically significant) in the incidence of supernumerary rudimentary thoracic ribs when compared to controls. However, this finding was not considered biologically significant by the authors of the study since the incidence was within normal limits for these species.
In conclusion, DPnB is not maternally toxic, embryo- or fetotoxic, or teratogenic in Wistar rats receiving dermal doses up to 1.0
ml/kg-d during organogenesis (days 6 - 15). The NOAEL for maternal toxicity, embryo- or fetal toxicity, or developmental toxicity is 1.0 ml/kg-d (910 mg/kg-d) and a LOAEL was not established.
In a pilot study 0, 0.1, 0.3 or 1 ml DPnB was applied dermally to Wistar rats during gestation day 6 till 16. No mortalities were observed. The reproduction and litter data did not reveal any treatment related effect. From this study
it was concluded that DPnB at levels up to 1 ml (910 mg/kg bw) was not embryo/fetotoxic to rats.
This study was identified as key for this toxicity endpoint because of the methods followed (which were comprehensively
documented in the report). The report included GLP and Quality Assurance statements, signed by the Study Director
and Head of the QA Unit, respectively. The study report followed OECD Protocol 414: "Teratogenicity" (12 May 1981),
the numbers and type of test animals used and their husbandry conditions were as prescribed in the guidance.
Test material characterization was adequate. The amount of test material applied complied with guidance, the length of
the treatment period (organogenesis) was sufficient, and evaluation criteria and statistical methods were typical for
this type assay and adequately recorded.
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