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EC number: 270-071-2 | CAS number: 68409-99-4 A complex combination of hydrocarbons produced by the distillation of products from the catalytic cracking process. It consists of hydrocarbons having carbon numbers predominantly in the range of C3 through C5 and boiling in the range of approximately -48°C to 32°C (-54°F to 90°F).
- 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
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP compliant, guideline study, available as unpublished report, no restrictions, fully adequate for assessment
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 997
- Report date:
- 1997
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- other: OECD Guideline 421 (Reproduction / Developmental Toxicity Screening Test)
- GLP compliance:
- yes (incl. QA statement)
- Limit test:
- no
Test material
- Reference substance name:
- Ethylene
- EC Number:
- 200-815-3
- EC Name:
- Ethylene
- Cas Number:
- 74-85-1
- Molecular formula:
- C2H4
- IUPAC Name:
- ethylene
- Details on test material:
- - Name of test material (as cited in study report): Compressed ethylene (technical grade)
- Supplied by: Linde Gas UK Ltd., Stoke on Trent, UK.
- Analytical purity: 99.94%
- Lot/batch No.: 50ST6299541
- Storage condition of test material: Steel container, outside at ambient temperature
Constituent 1
Test animals
- Species:
- rat
- Strain:
- other: Crl: CD BR
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River (UK) Ltd., Margate, UK
- Age at study initiation: approximately 9 weeks
- Weight at study initiation: 272.8-354.7 g (males), 194.9-248.7 g (females)
- Fasting period before study: No
- Housing: stainless steel wire-mesh suspended cages. From day 20 of gestation onwards in solid floor polypropylene cages with wire mesh stainless steel lids
- Diet: SQC Rat and Mouse Breeder Diet No 3, Expanded, Special Diet Services Ltd., Witham, UK ad libitum ( except during exposure)
- Water: mains drinking water ad libitum
- Acclimation period: 22 days
ENVIRONMENTAL CONDITIONS
- Temperature: 19-25°C
- Humidity: 40-70%
- Air changes: 15 per hr
- Photoperiod: 12hrs dark / 12hrs light
IN-LIFE DATES: From: 20 December 1995 To: 3 February 1996
Administration / exposure
- Route of administration:
- inhalation: gas
- Type of inhalation exposure (if applicable):
- head only
- Vehicle:
- other: air
- Details on exposure:
- Animals were exposed (head-only) in rodent restraint tubes secured to each of the two sides of the chamber through ports let into the chamber walls. Ethylene was ducted past the noses of the animals in a regulated flow and extracted from the chamber via ports at each end. The high dose concentration was generated through a miniature flowmeter and prepared in excess quantity of that needed for the high dose exposure. Balance of the flow served as a feedstock for the second stage of dilution for the low and intermediate doses.
Temperature and relative humidity in the exposure chamber was recorded 2 times/hour throughout the exposure period and monitored continuously using a digital thermometer and a paper hygrometer.
Chamber airflow was also monitored continuously with recordings twice per hour.
The air flow was maintained at a rate sufficient to provide the normal concentration of oxygen to the animals. The concentration of ethylene in each chamber was determined approximately 2 times per hour with a Miran 1A infrared spectrophotometer which was calibrated and the analytical concentration during each exposure was interpolated from the standard curve. - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- The ranges of mean daily concentrations of ethylene within the chambers were 187-243, 966-1082 and 4961-5171 ppm which were considered satisfactory.
- Details on mating procedure:
- - M/F ratio per cage: 1:1
- Length of cohabitation: when mating confirmed or 10 days
- Proof of pregnancy: vaginal plug / 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.
- After successful mating each pregnant female was caged individually - Duration of treatment / exposure:
- 6 hours/day, 7 days/week, 2 weeks prior to mating, during pairing, until the day prior to necropsy for the males (Day 28) or Day 20 of gestation for the females.
- Frequency of treatment:
- 6 hrs daily
- Duration of test:
- Approximately 28 days
- No. of animals per sex per dose:
- 10/sex/group
- Control animals:
- other: yes, air exposed
- Details on study design:
- Dose selection rationale: Following review of data from previous toxicity studies and based on levels that are safe in practice (high dose) and anticipated human exposure (low dose).
Examinations
- Maternal examinations:
- CAGE SIDE OBSERVATIONS: Yes
- Twice daily
DETAILED CLINICAL OBSERVATIONS: Yes
- Daily cage-side observations included mortality (twice daily), clinical reactions, abnormal behaviour, and availability of food and water. Post dosing observations were initially recorded up to 2 hours after the end of exposure; however, as no adverse clinical signs were seen on the first two days, the observations were conducted 0.5 and 1 hour after the end of exposure for the remainder of the week and immediately and 0.5 hours after the end of exposure for the remainder of the treatment period.
BODY WEIGHT: Yes
- Body weights were measured prior to the first treatment and weekly thereafter. Mated females were weighed on days 0, 7, 14, and 20 of gestation and on days 1 and 4 post-partum.
FOOD CONSUMPTION
Per cage of animals, food consumption was determined weekly during the pre-mating period. For mated females, food intake was recorded for days 0-4, 4-7, 7-10, 10-14, 14-17, and 17-20 of gestation and on days 1-4 post-partum.
LITTER DATA: Yes
For each female that littered the following were recorded: date of mating, date of parturition, duration of gestation, any abnormal behaviour. The following data were recorded for each litter: pup numbers (live and dead), number and sex of live pups recorded daily and reported for days 1 and 4 post-partum, clinical condition of pups on days 1-4 post-partum, individual pup weights on days 1 and 4, necropsy findings of dead pups.
POST MORTEM EXAMINATIONS:
At necropsy, all parental animals were subjected to macroscopic examination for structural or pathological changes. For each parental female, the numbers of corpora lutea and implantation sites were recorded. Blood samples were taken from all parental animals. 20 tissues were fixed and retained in formalin. Histopathological examination of the ovaries, testes and epididymides of the control and high dose group were conducted using light microscopy. - Ovaries and uterine content:
- The ovaries and uteri were examined after termination: Yes
Examinations included:
- Gravid uterus weight: No
- Number of corpora lutea: Yes
- Number of implantations: No
- Number of early resorptions: No
- Number of late resorptions: No - Fetal examinations:
- - External examinations: Yes: all per litter
- Soft tissue examinations: No
- Skeletal examinations: No
- Head examinations: No - Statistics:
- Body weights, body weight gains, and food intake were analyzed by analysis of variance. To test for equality of variances between groups, Levene's test was performed. Dunnett's test was used to compare each group and control. Regression analysis was performed for dose-response. Non-parametric analysis was used to evaluate the number of implantation sites, number of pups born, % male pups on days 1 and 4, post-implantation survival index, mean pup weights on days 1 and 4 and % weight change on days 1 and 4. This included Kruskall-Wallis analysis together with the protected Wilcoxon Rank Sum test for each treated group against control. The Terpstra-Jonckheere test for dose response was also performed. The Cochran-Armitage test for dose-response between groups and Fisher-Irwin tests for pairwise comparisons between control and treated groups were performed where data included a high proportion of tied values. This included mating index, mean duration of gestation, pup deaths on days 0-1, and 1-4, live birth index and viability index. Group values for fertility, fecundity, number of females with live pups at day 4, and gestation index were identical and therefore were not analyzed.
- Indices:
- Reproductive function was evaluated by calculation of mating index, female and male fecundity index, and female and male fertility index. In addition, the gestation index, post implantation survival index, live birth index, viability index and % male pups was calculated.
Results and discussion
Results: maternal animals
Maternal developmental toxicity
- Details on maternal toxic effects:
- Maternal toxic effects:no effects
Effect levels (maternal animals)
open allclose all
- Key result
- Dose descriptor:
- NOAEC
- Effect level:
- 5 000 ppm
- Basis for effect level:
- other: maternal toxicity
- Key result
- Dose descriptor:
- NOAEC
- Effect level:
- 5 737 mg/m³ air
- Basis for effect level:
- other: maternal toxicity
Results (fetuses)
- Details on embryotoxic / teratogenic effects:
- Embryotoxic / teratogenic effects:no effects
Effect levels (fetuses)
open allclose all
- Dose descriptor:
- NOAEC
- Effect level:
- 5 000 ppm
- Basis for effect level:
- other: Developmental Toxicity
- Key result
- Dose descriptor:
- NOAEC
- Effect level:
- 5 737 mg/m³ air
- Basis for effect level:
- other: Developmental Toxicity
Fetal abnormalities
- Abnormalities:
- not specified
Overall developmental toxicity
- Developmental effects observed:
- not specified
Any other information on results incl. tables
Fertility:
No deaths were observed that were attributable to treatment. Clinical observations did not indicate an adverse effect of treatment. Observations included minor changes such as swollen ears, damaged or missing tip of tail or ear, sores and lesions chromodacryorrhoea, hair loss, etc. Of note, several females in all groups during the latter half of the gestation period showed a red discharge from the vulva which was attributed to the restraint method which prevented normal grooming behaviours. No adverse outcome on pregnancy was observed.
In females (early gestation, days 0-7) from the low dose group, a significant increase in body weight was observed as compared to controls. Treatment was not seen to adversely affect body weight gain of males or females during premating, or females during gestation or lactation at any of the doses. Food intake of treated males and females during pre-pairing (males and females) as well as gestation and lactation (females only) was unaffected. For females treated with the high dose, food intake was shown to be significantly increased for days 1-4 of lactation.
There were no ethylene-induced effects on fertility or fecundity. All females became pregnant.
Mean number of corpora lutea and implantation sites per dam was seen to be slightly higher than controls in all treatment groups, although this effect was not statistically significant.
The post-implantation survival index was slightly lower in the treated groups; however no adverse effect on litter size was seen.
Developmental Parameters:
Litter parameters were unaffected by ethylene treatment. The number of pups alive on days 1 and 4 in all treatment groups was no different from control. The % of male pups (sex ratio) in all treatment groups on day 1 and 4 was similar to control. The live birth index and viability index were both unaffected by ethylene treatment.
Mean pup weights were seen to be higher than controls in all treated groups at days 1 and 4 post-partum, although this increase was not statistically significant.
Mean pup weights (g) male and female combined |
ethylene concentration (ppm) |
|||
0 |
200 |
1000 |
5000 |
|
Day 1 |
6.0 |
6.4 |
6.3 |
6.5 |
Day 4 |
8.6 |
9.1 |
8.9 |
9.2 |
% Weight change Day 1-4 |
43.3 |
42.2 |
41.3 |
41.5 |
Necropsy findings did not suggest toxicity due to ethylene treatment. Clinical observations on day 1 post-partum included findings attached umbilical cord, haemorrhagic; nose, hindpaw, abdomen, back, and mouth, pups which were cold and unfed, etc. These findings were distributed equally among all experimental groups including control. At necropsy, on post-partum day 4, findings including pups without milk in the stomach, microphthalmia and damage of a tail tip. Again, these findings were not attributed to ethylene treatment.
Applicant's summary and conclusion
- Conclusions:
- Head-only exposure of rats to ethylene at concentrations of 0, 200, 1000, or 5000 ppm did not induce effects on reproductive performance, fertility, or pregnancy. The NOAEC in this study was 5000 ppm (5737 mg/m3).
- Executive summary:
The potential effects of ethylene inhalation on rat reproduction and on growth and development of the offspring was studied in a combined reproduction/development toxicity screening test, conducted according to GLP. Four groups of rats (10 females and 10 males per group) were dosed by head only inhalation for 6 hours daily with air only (control); 200, 1000 or 5000 ppm of ethylene (corresponding to 0, 230, 1147 or 5737 mg/m3). Ethylene was administered to parent animals for two weeks prior to mating, during the mating period and until the day prior to necropsy of the males (minimum 28 days) or until day 20 of gestation for the females. The females were allowed to litter and rear their offspring to day 4 post-partum, when they and their offspring were killed. Morbidity, mortality, clinical condition, weight and food intake were observed throughout the study, and mating was carefully observed. For each female, litter data and also observations for each offspring were recorded. At termination of the study, all animals were subject to macroscopic examination for structural or pathological changes.
There were no deaths attributable to the test article, and body weight gain was not adversely affected during the pre-mating, gestation or lactation periods. The treatment had no effect on fertility or fecundity and all females became pregnant. Litter size, sex ratio, mean pup weight and pup growth and clinical condition were not adversely affected by treatment. Necropsy revealed no macroscopic finding suggestive of toxicity due to test substance administration. There was no evidence of any toxic effect on the testis due to test substance administration and there were no other microscopic findings suggestive of toxicity due to the exposure.
In conclusion, head-only administration of ethylene at nominal concentrations of 200, 1000 or 5000 ppm was without evidence of toxicity or adverse effects on growth and development of the offspring from conception to day 4 post-partum.
The highest dose of 5000 ppm (5736 mg/m3) is concluded to be a no adverse effect concentration (NOAEC) for the reproduction/development screening test in rats.
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