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EC number: 204-685-9 | CAS number: 124-17-4
- 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:
- 1985
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: A published study which is sufficiently well reported to be able to judge it as reliable for risk assessment purposes for this end point.
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Reference
- Endpoint:
- one-generation reproductive toxicity
- Remarks:
- based on test type (migrated information)
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Study period:
- 1984
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: A published study which contains sufficient experimental detail to be able to judge it as reliable. No sperm parameters were directly examined although the design of the study was capable of detecting sperm function deficiencies.
- Reason / purpose for cross-reference:
- reference to same study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 415 [One-Generation Reproduction Toxicity Study (before 9 October 2017)]
- Deviations:
- no
- Remarks:
- specific deviations noted
- GLP compliance:
- not specified
- Limit test:
- no
- Species:
- rat
- Strain:
- other: Charles River CD
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Laboratories
- Age at study initiation: males: 28 days, females :70 days
- Weight at study initiation: (P) Males: 190 +/16g approx all within 1.6 standard deviations ; Females: 240+/-14g approx, all within 1.5 standard deviations.
- Fasting period before study: none
- Housing: Environmentally controlled room, individually housed in suspended wire cages except during mating, gestation and lactation.
- Diet (ad libitum): Purina labs certified rodent chow 5002
- Water (ad libitum): tap
- Acclimation and observation period: 15 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20-24C
- Humidity (%): 20-70%
- Air changes (per hr): no data
- Photoperiod (hrs dark / hrs light): fluorescent light 12hrs light/12hrs dark - Route of administration:
- oral: gavage
- Vehicle:
- water
- Details on exposure:
- VEHICLE
- Amount of vehicle (if gavage): 5ml - Details on mating procedure:
- - M/F ratio per cage: 1:1
- Proof of pregnancy: vaginal plug or sperm in vaginal smear referred to as day 0 of pregnancy
- After 10 days of unsuccessful pairing replacement of first male by another male with proven fertility for a further 5 days.
- After successful mating each pregnant female was placed in a separate plastic cage.
- Other: cross-over design used. - Analytical verification of doses or concentrations:
- no
- Duration of treatment / exposure:
- Premating exposure period (males): 60 days
Premating exposure period (females): 14 days , then treatment until GD13 sacrifice timepoint or weaning of offspring.
Duration of test: 101 days - Frequency of treatment:
- daily
- Details on study schedule:
- no further information
- Dose / conc.:
- 250 mg/kg bw/day
- Dose / conc.:
- 500 mg/kg bw/day
- Dose / conc.:
- 1 000 mg/kg bw/day
- No. of animals per sex per dose:
- 25
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Other: A cross-over design was used. See table below for design.
- Positive control:
- No
- Parental animals: Observations and examinations:
- CAGE SIDE OBSERVATIONS: No data
DETAILED CLINICAL OBSERVATIONS: No data
BODY WEIGHT: Yes
- Time schedule for examinations: weekly. Females on GD0, 1, 13 and 20 and lactation days 0, 7, 14 and 21. - Oestrous cyclicity (parental animals):
- not examined
- Sperm parameters (parental animals):
- No sperm parameters examined. Number of fertile males recorded.
- Litter observations:
- STANDARDISATION OF LITTERS
- Performed on day 4 postpartum: yes
- If yes, maximum of 10 pups/litter (5/sex/litter as nearly as possible); excess pups were selected randomly, killed and discarded.
PARAMETERS EXAMINED
The following parameters were examined in F1 offspring: stillbirths, live births, postnatal mortality, presence of gross anomalies, weight gain
OTHER
- Litters were observed daily for gross signs of toxicity, changes in appearance, behaviour or mortality. - Postmortem examinations (parental animals):
- SACRIFICE (by CO2 asphyxiation)
- Male animals: All surviving animals at GD13 timepoint for females
- Maternal animals: All surviving animals 25 days after separation from males.
OTHER
For females sacrificed on GD13, intrauterine examination was performed and number of corpora lutea, implants, resorptions, and viable embryos recorded. Nongravid animal uterii were examined for evidence of early resorptions. All animals were examined externally but internal examinations were only carried out on those that died early. - Postmortem examinations (offspring):
- SACRIFICE
- The F1 offspring were sacrificed at 21 days of age.
GROSS NECROPSY
- Gross necropsy consisted of external examinations for signs of gross abnormalities - Statistics:
- Comparison of treated to untreated groups at p<0.5 using Mann-Whitney U test (comparison of postimplantation losses), fertlility indices using Chi square test with Yates correction and/or Fishers exact test and all other parameters using Barlett's test for homogeneity and Student's t test.
- Reproductive indices:
- not calculated
- Offspring viability indices:
- not calculated
- Clinical signs:
- no effects observed
- Body weight and weight changes:
- no effects observed
- Food consumption and compound intake (if feeding study):
- no effects observed
- Organ weight findings including organ / body weight ratios:
- not specified
- Reproductive function: oestrous cycle:
- not specified
- Reproductive function: sperm measures:
- not specified
- Reproductive performance:
- no effects observed
- Description (incidence and severity):
- Fertility of males and females was not affected. There were no effects on resorptions, live/dead embryo ratios, viability, corpora lutea or implants
- Remarks on result:
- not determinable due to absence of adverse toxic effects
- Clinical signs:
- no effects observed
- Mortality / viability:
- no mortality observed
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- The only statistically significant finding was a reduction in pup weight gain at the highest dosed tested in the treated females/untreated males group, suggesting slight toxicity to the neonate. This was only seen at GD14 and was not observed at the time points either side (GD4 and GD21).
- Sexual maturation:
- not specified
- Organ weight findings including organ / body weight ratios:
- not specified
- Gross pathological findings:
- not specified
- Histopathological findings:
- not specified
- Dose descriptor:
- NOAEL
- Generation:
- F1
- Effect level:
- 500 mg/kg bw/day
- Sex:
- male/female
- Basis for effect level:
- body weight and weight gain
- Reproductive effects observed:
- not specified
- Conclusions:
- Diethylene glycol is not toxic to the fertility of male or female rats at doses up to 1000mg/kg
- Executive summary:
In a well conducted single generation fertility study which conformed to the basic requirements of an OECD guideline study, 2 -(2 -butoxyethoxy)ethanol produced no signs of toxicity to reproduction in either male or female rats when tested at oral doses up to 1000mg/kg. The only finding that was attributed to treatment was a small but statistically significant reduction in pup weight gain seen at the highest dose tested and at a single time point during gestation. The minor and transient nature of this finding is not deemed biologically significant.
Synopsis
Not toxic to reproduction
Data source
Reference
- Reference Type:
- publication
- Title:
- Fertility and teratogenic studies of diethylene glycol monobutyl ether in rats and rabbits
- Author:
- Nolen GA, Gibson WB, Benedict JH, Briggs DW, Schardein JL
- Year:
- 1 985
- Bibliographic source:
- Fund appl. Toxicol. 5, 1137.
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- Deviations:
- no
- Remarks:
- significant deviations noted
- GLP compliance:
- not specified
- Limit test:
- no
Test material
- Reference substance name:
- 2-(2-butoxyethoxy)ethanol
- EC Number:
- 203-961-6
- EC Name:
- 2-(2-butoxyethoxy)ethanol
- Cas Number:
- 112-34-5
- Molecular formula:
- C8H18O3
- IUPAC Name:
- 2-(2-butoxyethoxy)ethanol
- Details on test material:
- - Name of test material (as cited in study report): diethylene glycol monobutyl ether.
- Analytical purity: 95% +/-2% as determined by gas chromatography. IR spectrum was identical to a 98.5% pure reference standard.
- Other: supplied by Union Carbide Company.
Constituent 1
Test animals
- Species:
- rabbit
- Strain:
- New Zealand White
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Langshaw Farms Inc, Augusta, MI
- Age at study initiation: 5 months
- Housing: individually in suspended wire cages
- Diet ad libitum: Purina certified rabbit chow 5322
- Water: tap, ad libitum
- Acclimation period: 72 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20-24
- Humidity (%): 20-70 with an occasional fluctuation to 78.
- Photoperiod (hrs dark / hrs light): 12/12. Received 30mg/USgal of 12.5% sodium sulphamethazine in drinking water for 7 days 6 weeks before study commenced.
Administration / exposure
- Route of administration:
- dermal
- Vehicle:
- water
- Details on exposure:
- TEST SITE
- Area of exposure: 10x20cm
- Type of wrap if used: no data. Not occluded, no wrap
- Time intervals for shavings or clipplings: prior to initial treatment and then weekly clipped.
REMOVAL OF TEST SUBSTANCE
- Washing (if done): Yes, warm water then dried by towel.
- Time after start of exposure: 4 hours
TEST MATERIAL
- Amount(s) applied (volume or weight with unit): 3ml/kg
- Concentration (if solution): no data
- Constant volume or concentration used: yes, 3ml/kg
VEHICLE
- Amount(s) applied (volume or weight with unit): 3ml/kg
- Concentration (if solution): no data
USE OF RESTRAINERS FOR PREVENTING INGESTION: yes, collars during exposure period - Analytical verification of doses or concentrations:
- not specified
- Details on mating procedure:
- - Impregnation procedure: artificial insemination. 3 weeks prior to insemination, does superovulated by injection of 50 USP of chorionic gonadotropin. 10 male rabbits used as semen donors - ejaculated using artificial vaginas. Ejaculate checked to ensure >60% motile before use. Equal numbers of does inseminated from each buck. After insemination, does given 100DUS of chorionic gonadotropin to ensure ovulation.
- Proof of pregnancy: Day of insemination taken as GD0 - Duration of treatment / exposure:
- days 8 to 19 of gestation
- Frequency of treatment:
- 4 hours/day
- Duration of test:
- to GD 19
Doses / concentrationsopen allclose all
- Dose / conc.:
- 100 mg/kg bw/day (nominal)
- Dose / conc.:
- 300 mg/kg bw/day (nominal)
- Dose / conc.:
- 1 000 mg/kg bw/day (nominal)
- No. of animals per sex per dose:
- 20
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Rationale for animal assignment (if not random): Animals distributed amongst test groups by weight to ensure mean body weights within 2.9SD of means.
Examinations
- Maternal examinations:
- CAGE SIDE OBSERVATIONS: No data
DETAILED CLINICAL OBSERVATIONS: No data
BODY WEIGHT: Yes
- Time schedule for examinations: every 3 days beginning GD0
FOOD CONSUMPTION: Yes, daily
POST-MORTEM EXAMINATIONS: Yes / No / No data
- Sacrifice on gestation day 29 by sodium pentobarbital
- Organs examined: no data - Ovaries and uterine content:
- The ovaries and uterine content was examined after termination: Yes
Examinations included:
- Gravid uterus weight: No data
- Number of corpora lutea: Yes
- Number of implantations: Yes
- Number of resorptions: Yes
- other: number of vialble and non viable fetuses. - Fetal examinations:
- - External examinations: Yes
- Soft tissue examinations: Yes: by the method of Staples RE (Teratol, 9, A37-8, 1974)
- Skeletal examinations: Yes: by Alizarin red S (Dawson AB, Stain Technol 1, 123-4 (1926)
- Head examinations: No data
Other: weighed, sexed. Fetal findings classified as malformations or variations. - Statistics:
- Comparison of treated to control groups. Feed consumption, corpora lutea, implants, resorptions, viable fetuses fetal and, body weights by ANOVA with Bartlett's test for homogeneity and appropriate t-test for variance equality. Regression analysis on dose levels. Fetal abnormalities by Fisher's exact test. Significance set at p<0.05.
- Indices:
- not reported
- Historical control data:
- not reported
Results and discussion
Results: maternal animals
General toxicity (maternal animals)
- Dermal irritation (if dermal study):
- effects observed, treatment-related
- Description (incidence and severity):
- For local skin effects see table 1.
- Mortality:
- no mortality observed
- Body weight and weight changes:
- effects observed, non-treatment-related
- Description (incidence and severity):
- All treated dams showed reduced weight gain but only the mid dose group reached statistical significance and there was clearly no dose respose relationship. The standard deviations of the treated animals were >50% of the means. These effects were not thought to be related to the amount of dose absorbed.
Effect levels (maternal animals)
open allclose all
- Dose descriptor:
- NOAEL
- Effect level:
- > 1 000 mg/kg bw/day
- Basis for effect level:
- other: maternal toxicity
- Remarks on result:
- other: No adverse effects observed
- Dose descriptor:
- NOAEL
- Effect level:
- > 100 - < 300 mg/kg bw (total dose)
- Basis for effect level:
- other: other:
Results (fetuses)
- Details on embryotoxic / teratogenic effects:
- Occasional isolated effects in single dams across dose groups was not attributed to treatment (one abortion in high dose group, 1 early delivery in mid dose group). There were no significant differences seen in the mean numbers of corpora lutea, implants, resorptions or viable foetuses or in the mean foetal body weight. and incidence of skeletal anomalies or of gross or visceral malformations.
Effect levels (fetuses)
- Remarks on result:
- not determinable due to absence of adverse toxic effects
Fetal abnormalities
- Abnormalities:
- no effects observed
Overall developmental toxicity
- Developmental effects observed:
- not specified
Any other information on results incl. tables
Skin irritancy was noted as follows after approximately one week of treatment and persisted until sacrifice:
Dose group: | Control and 100mg/kg | 300mg/kg | 1000mg/kg |
Findings: | No effects | 6/20 slight erythema5/20 desquamation | All animals showed moderate irritation (edema, fissuring, coriaceousness) |
Applicant's summary and conclusion
- Conclusions:
- 2-(2-butoxyethoxy)ethanol is not teratogenic by the dermal route of exposure
- Executive summary:
In a well conducted teratology study which conformed to the basic OECD guideline requirements, 2 -(2 -butoxyethoxy)ethanol produced no signs of developmental toxicity when tested at doses up to 1000mg/kg bw/day applied by the dermal route. The only finding that was clearly attributed to treatment was significant irritation at the site of application manifest at doses from 300mg/kg bw/day upwards. There was some evidence for a reduction in maternal body weight gain, but this was only significant in the mid dose animals and there was no clear dose response relationship.
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