Butene

Toxicity to reproduction

Administrative data

Endpoint:

screening for reproductive / developmental toxicity

Remarks:

based on test type (migrated information)

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other: GLP compliant, guideline study, available as unpublished report, fully adequate for assessment

Cross-reference

Cross-reference 1

Reason / purpose for cross-reference:

reference to same study

Cross-reference 2

Reason / purpose for cross-reference:

reference to other study

Data source

Reference

Reference Type:

study report

Title:

Unnamed

Year:

2003

Report date:

2003

Materials and methods

Test guideline

Qualifier:

according to guideline

Guideline:

OECD Guideline 422 (Combined Repeated Dose Toxicity Study with the Reproduction / Developmental Toxicity Screening Test)

Deviations:

no

Principles of method if other than guideline:

Not applicable

GLP compliance:

yes

Limit test:

no

Test material

Test material information

Constituent 1

Reference substance name:

1-butene

Cas Number:

106-98-9

Molecular formula:

C4H8

IUPAC Name:

1-butene

Details on test material:

- Name of test material (as cited in study report): 1-butene
- Analytical purity: ≥99%

Test animals

Species:

rat

Strain:

other: Crl:CD® (Sprague-Dawley) IGS BR

Sex:

male/female

Details on test animals or test system and environmental conditions:

- Source: Charles River Laboratories, Kingston, New York, USA.
- Age at study initiation: c.a. 8 weeks
- Weight at study initiation: Males 200-300g, females 150-250 g
- Housing: Individually in stainless steel, wire mesh cages within a 1.0 m3 glass and stainless steel whole body exposure chamber except during the mating period when one male and one female were housed together in a cage of suitable size.
- Diet: Certified Rodent Diet No. 5002 (PMI Nutrition International, St. Louis, MO) ad libitum except during exposure
- Water: Mains water ad libitum except during exposure.
- Acclimation period: Approximately 2 weeks

ENVIRONMENTAL CONDITIONS
- Temperature: 20-25°C
- Humidity: 36-82%
- Air changes: Not reported
- Photoperiod: 12 hrs dark / 12 hrs light

IN-LIFE DATES: From: 1 July 2002 To: 25 August 2002

Administration / exposure

Route of administration:

inhalation: gas

Type of inhalation exposure (if applicable):

whole body

Vehicle:

other: air

Details on exposure:

GENERATION OF TEST ATMOSPHERE / CHAMBER DESCRIPTION
The whole-body exposure chambers each had a volume of approximately 1000 L. The chambers was operated at a minimum flow rate of 200 L/minute. The final airflow was set to provide at least one air change in 5.0 minutes (12 air changes/hour) and a T99 equilibrium time of at most 23 minutes At the end of the 6-hour exposure, all animals remained in the chambers for a minimum of 30 minutes. During this time, the chambers were operated at approximately the same flow rate using clean air only. The chambers were exhausted through the in housed filtering system, which consisted of a coarse filter, a HEPA filter and activated charcoal.
For the treated groups, the test article was delivered from the cylinder via a regulator with a backpressure gauge via 1/4" tubing through a flowmeter via 1/4" tubing. The outlet of the flowmeter was regulated by a built-in metering valve. The test article laden airstream was directed into the turret of a 1.0 m3 glass and stainless steel exposure chamber via 1/4" tubing, where it was diluted with room air as it was drawn into the chamber. For controls, room air was drawn into the turret of the 1.0 m3 glass and stainless steel exposure chamber.



TEST ATMOSPHERE
During each exposure, measurements of airborne concentrations were performed in the animals' breathing zone at least 4 times using an appropriate sampling procedure and on-line GC analytical method. During each week of exposure, particle size determinations were performed using a TSI Aerodynamic Particle Sizer to characterize the aerodynamic particle size distribution of any aerosol present.

Details on mating procedure:

- M/F ratio per cage: 1 male and 1 female
- Length of cohabitation: until evidence of mating seen or for 2 weeks
- Proof of pregnancy: vaginal plug / sperm in vaginal smear referred to as day 0 of pregnancy
- After successful mating each pregnant female was caged Individually

Analytical verification of doses or concentrations:

yes

Details on analytical verification of doses or concentrations:

The mean (± standard deviation) analytical (GC) concentrations for the control and the exposure groups were as follows: 0 ± 0, 524 ± 40, 2062 ± 126 and 8271 ± 683 ppm. The analytically measured exposure levels of the airborne test article were reasonably close to the targeted exposure levels.

Duration of treatment / exposure:

Two weeks prior to breeding, during breeding, and continuing through day 19 of gestation. The dams were then allowed to deliver their litters, which were retained until lactation day 4.

Frequency of treatment:

6 hours/day, 7 days/week

Details on study schedule:

see below

Doses / concentrations

Doses / concentrations 1

Remarks:

Doses / Concentrations:
0, 500, 2000, or 8000 ppm
Basis:
other: target concentrations

Doses / concentrations 2

Remarks:

Doses / Concentrations:
0 ± 0, 524 ± 40, 2062 ± 126 and 8271 ± 683 ppm
Basis:
analytical conc.

No. of animals per sex per dose:

12

Control animals:

yes, sham-exposed

Details on study design:

MMAD: 0.822 ± 0.1, 0.893 ± 0.2, 0.7986 ± 0.0343 and 3.6503 ± 7.0 for 0, 500, 2000 and 8000 ppm respectively
GSD: 2.019 ± 0.4, 1.869 ± 0.3, 1.893 ± 0.3 and 2.181 ± 0.8 for 0, 500, 2000 and 8000 ppm respectively

Positive control:

none

Examinations

Parental animals: Observations and examinations:

CAGE SIDE OBSERVATIONS: Yes
- Time schedule: At least twice/day

DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: Females weekly during pre-mating and on gestations days 0, 7, 14, 20 and lactation days 0, 1 and 4.

BODY WEIGHT: Yes
- Time schedule: Females day treatment initiated, twice/week until copulation confirmed, gestations days 0, 7, 14 and 20, lactation days 1 and 4. Females without evidence of mating were weighed weekly. All weighed at termination.

FOOD CONSUMPTION: Yes
- Time schedule: Females weekly during pre-mating period, gestation days 0-7, 7-14, 14-20 and lactation days 1-4.

Oestrous cyclicity (parental animals):

not determined

Sperm parameters (parental animals):

not determined

Litter observations:

STANDARDISATION OF LITTERS
- Performed on day 4 postpartum: No

PARAMETERS EXAMINED
The following parameters were examined as soon as possible after parturition and twice / day thereafter: number of live and dead pups and sex of pups, physical or behavioural abnormalities.

GROSS EXAMINATION OF DEAD PUPS:
yes, for external and internal abnormalities and presence/absence of milk in stomach

Postmortem examinations (parental animals):

SACRIFICE
- Maternal animals: Mated animals on day 5 post partum, animals when evidence of mating was detected but failed to deliver 26 days after evidence of mating, animals with no evidence of mating 26 days after completion of mating period.

GROSS NECROPSY
- Maternal animals: Gross necropsy consisted of external and internal examinations including the cervical, thoracic, and abdominal viscera. Number of implantation sites and corpora lutea were assessed.

ORGAN WEIGHTS
Maternal animals: ovaries with oviducts, uterus with vagina, adrenals, brain with brainstem, heart, kidneys, liver, thymus, spleen, lungs.

MICROSCOPIC EXAMINATION: No

Postmortem examinations (offspring):

External macroscopic postmortem examinations performed on all F1 pups found dead during lactation and at termination on lactation day 4. No microscopic examination of pups.

Statistics:

Mean values of all exposure groups were compared to the mean value for the control group at each time interval. For all parameters except for organ weights, the standard one-way analysis of variance (ANOVA) using the F ratio to assess significance was used. If significant differences among the means were indicated, additional testing was performed using Dunnett's t-test to determine which means were significantly different from the control. Organ weight data was analyzed only by parametric methods. Bartlett's test was performed to determine if groups had equal variances. The standard
one-way analysis of variance (ANOVA) using the F ratio to assess significance was used. If significant differences among the means were indicated, additional tests were used to determine which means were significantly different from the control: Dunnett's t-test for homogeneous data, or Cochran and Cox's modified t-test for non-homogeneous data. All t-tests were conducted at the 5% and 1% significance levels. For incidence data, a Fisher Exact Test with Bonferonni correction was performed to identify differences between the control and treatment groups.

Reproductive indices:

Gonadal function, mating behaviour, implantation, and general fertility were evaluated.

Offspring viability indices:

Litter size, pup survival, sex, body weight, and the presence of gross external malformations were assessed in the offspring.

Results and discussion

Results: P0 (first parental generation)

General toxicity (P0)

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:

no effects observed

Histopathological findings: non-neoplastic:

no effects observed

Other effects:

not specified

Reproductive function / performance (P0)

Reproductive function: oestrous cycle:

not examined

Reproductive function: sperm measures:

not examined

Reproductive performance:

no effects observed

Details on results (P0)

see below

Effect levels (P0)

Dose descriptor:

NOAEC

Effect level:

8 000 other: (18359 mg/m3, 18.4 mg/m3) nominal

Sex:

male/female

Basis for effect level:

other: no treatment-related effects on dams at the highest concentration tested. No effects on reproductive performance or fertility

Results: F1 generation

General toxicity (F1)

Clinical signs:

no effects observed

Mortality / viability:

no mortality observed

Body weight and weight changes:

no effects observed

Sexual maturation:

not examined

Organ weight findings including organ / body weight ratios:

not examined

Gross pathological findings:

no effects observed

Details on results (F1)

see below

Effect levels (F1)

Dose descriptor:

NOAEC

Generation:

F1

Effect level:

8 000 other: (18359 mg/m3, 18.4 mg/L) nominal

Sex:

male/female

Basis for effect level:

other: no treatment-related effects on pups at the highest concentration tested. No effects on pup viability, body weight or development

Overall reproductive toxicity

Reproductive effects observed:

not specified

Any other information on results incl. tables

All mated female animals (except one animal in the 2000 ppm group) were found pregnant and delivered live pups. Mating indices for the male rats treated with the test article were comparable to controls. Mating, fertility and gestation indices for the female rats treated with the test article were comparable to controls. Most of the females mated at the first opportunity. There were also no treatment-related differences in the other reproductive parameters up to the time of parturition including the percent of females completing delivery and the duration of gestation, when compared to controls. There were no treatment related differences in all parturition parameters including the total number of pups delivered, the number of pups dying, the viability (4 day survival) index, the number of implantation sites and corpora lutea per dam, the pup sex ratio and the number of live pups/litter, when compared to controls.

Applicant's summary and conclusion

Conclusions:

Repeated inhalation exposure of 1-butene to female Sprague Dawley rats at levels of 0, 500, 2000, or 8000 ppm produced no evidence of adverse effects on any measures of reproductive function.

Executive summary:

Male and female rats were exposed to 1-butene at target concentrations of 500, 2000, 8000 ppm (1147, 4589, 18359 mg/m3) for two weeks prior to breeding, during breeding and until day 19 of gestation. The dams were then allowed to deliver their litters, which were retained until post-natal day 4. There was no evidence of systemic toxicity in the parents.There were no effects on mating behaviour, fertility and gestation indices, the number of implantation sites and corpora lutea per dam, numbers of pups delivered, viability of pups at and after birth and the pup sex ratio when compared to the control group. Based on these data, the NOAEC for reproductive toxicity was the highest concentration tested (18359 mg/m3). There were no treatment-related effects on the development of pups. There were no effects on body weight gain or observed during macroscopic examination of pups at post mortem. Based on these data, the NOAEC for developmental toxicity was also the highest concentration tested (18359 mg/m3).