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EC number: 205-563-8 | CAS number: 142-82-5
- 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
![](https://poisoncentres.echa.europa.eu/o/diss-blank-theme/images/factsheets/A-REACH/factsheet/print_toxicological-information.png)
Toxicity to reproduction
Administrative data
- Endpoint:
- two-generation reproductive toxicity
- Remarks:
- based on test type
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- 18 Sept 1989 - 16 June 1990
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Comparable to guideline study.
- Justification for type of information:
- A discussion and report on the read across strategy is given as an attachment in IUCLID Section 13.
Cross-reference
- Reason / purpose for cross-reference:
- read-across: supporting information
Reference
- Endpoint:
- two-generation reproductive toxicity
- Remarks:
- based on test type
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- 18 Sept 1989 - 16 June 1990
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Comparable to guideline study.
- Justification for type of information:
- A discussion and report on the read across strategy is given as an attachment in IUCLID Section 13.
- Reason / purpose for cross-reference:
- read-across source
- Species:
- rat
- Key result
- Dose descriptor:
- NOAEC
- Effect level:
- 31 680 mg/m³ air (nominal)
- Sex:
- male/female
- Basis for effect level:
- other: The value was re-calculated from the nominal dose of 9000 ppm.
- Remarks on result:
- other: Generation: reproductive toxicity
- Key result
- Dose descriptor:
- NOAEC
- Effect level:
- 10 560 mg/m³ air (nominal)
- Sex:
- male/female
- Basis for effect level:
- other: reduced body weight. The value was re-calculated from the nominal dose of 3000 ppm
- Remarks on result:
- other: Generation F1, F2
- Key result
- Dose descriptor:
- LOAEC
- Effect level:
- 31 680 mg/m³ air (nominal)
- Sex:
- male/female
- Basis for effect level:
- other: reduced body weight. The value was recalculated from the nominal dose of 9000 ppm
- Remarks on result:
- other: Generation F1, F2
- Key result
- Reproductive effects observed:
- not specified
- Conclusions:
- The NOAEC for both male and female rats (adults and offspring) was 3000 ppm. The LOAEC for these groups was 9000 ppm based on reduced body weight. There were no adverse effects on reproduction, therefore the NOAEC for reproduction is 9000 ppm.
- Executive summary:
This data is being read across from the source study that tested commercial hexane based on analogue read across.
The purpose of this study was to determine the effect of commercial hexane on reproduction in rats. Groups of 25 male and 25 female rats were exposed to nominal concentrations of 0, 900, 3000, or 9000 ppm of test substance for 10 weeks pre-breeding, 3 weeks during breeding, and postnatal days 4 -28. After weaning, pups were selected to be parents for the F2 generations, and treated similarly to their parents, except their pre-breeding exposure was 8 weeks. During exposure, animals were monitored for mortality, clinical signs, food consumption, and body weight. Offspring were examined for body weight, survival, and viability. Both parents and offspring were sacrificed and examined for gross abnormalities, and in the case of adults histopathology. Reproductive parameters were similar in exposure groups and control groups. There was reduced body weight in the F1 and F2 generation in both sexes in the 9000 ppm exposure group in both adults and offspring. The NOAEC is therefore 3000 ppm, and the LOAEC is 9000 ppm. Since there were no adverse effects in offspring without adverse maternal effects, the NOAEC for reproduction is 9000 ppm.
CLINICAL SIGNS AND MORTALITY (PARENTAL ANIMALS)
No treatment related effects observed.
BODY WEIGHT AND FOOD CONSUMPTION (PARENTAL ANIMALS)
There were no treatment related effects on food consumption. Males in the 9000 ppm group had reduced body weight during week 13. Body weight gains in this group were reduced during weeks 7, 11-12, and 12-13. Males in the 3000 ppm group had reduced body weight gain in weeks 4-5, and reduced weight in weeks 9-10. Females weight gains were reduced in the 9000 ppm group in weeks 5-6.
REPRODUCTIVE PERFORMANCE (PARENTAL ANIMALS)
Lactational food consumption was significantly reduced during days 7-11, and days 19-21 in the 9000 ppm group. No other reproductive parameters differed significantly from controls.
GROSS PATHOLOGY (PARENTAL ANIMALS)
No treatment related abnormalities were seen.
HISTOPATHOLOGY (PARENTAL ANIMALS)
Hyaline droplet nephropathy and tubular basophilia were seen in the 9000 ppm males.
F1 GENERATION
CLINICAL SIGNS AND MORTALITY (PARENTAL ANIMALS)
No treatment related effects were observed. One female in the 900 ppm group died on day 83 due to prolonged delivery.
BODY WEIGHT AND FOOD CONSUMPTION (PARENTAL ANIMALS)
Body weights of 9000 ppm males were significantly reduced throughout the exposure period. Weight gain was reduced in this group during the weeks 9-10, and 10-11. Females in the 9000 ppm group had reduced body weight during the first 3 weeks of pre-breeding exposure.
REPRODUCTIVE PERFORMANCE (PARENTAL ANIMALS)
In the 9000 ppm group, food consumption was reduced on gestational days 0-4, and 4-7, and gestational intervals 0-7, and 7-14. This group also had reduced food consumption during lactational days 21-24, 26-27, 21, and 28. In the 3000 ppm group, food consumption was reduced during lactational days 22-23, and in the 900 ppm group during days lactational days 21-22.
GROSS PATHOLOGY (PARENTAL ANIMALS)
No treatment related abnormalities were seen.
HISTOPATHOLOGY (PARENTAL ANIMALS)
Hyaline droplet nephropathy and tubular basophilia were seen in the 9000 ppm males.
VIABILITY (OFFSPRING)
The number of dead pups was increased in the 900 ppm exposure group, however, as this was not seen at higher doses, it was not considered treatment related.
BODY WEIGHT (OFFSPRING)
The body weight of pups in the 9000 ppm group were reduced beginning on lactational day 14. Body weight gains in this group were reduced during lactational days 14-21 for females, and lactational days 7-14 for all pups.
GROSS PATHOLOGY (OFFSPRING)
No treatment related effects were noted.
F2 GENERATION
VIABILITY (OFFSPRING)
Viability was unaffected by exposure.
BODY WEIGHT (OFFSPRING)
The body weight of pups in the 9000 ppm group were reduced from lactational day 7-28. Body weight gains in this group were reduced during lactational days 14-21 for females, and lactational days 7-14 for all pups. There were significantly reduced body weight gains in pups in the 9000 ppm group during lactational days 4-7, and 7-14, and slightly reduced weight gains on lactational days 14-21.
GROSS PATHOLOGY (OFFSPRING)
No treatment related effects were noted.
Significant Results of Reproductive Toxicity Study on Rats
Concentration (ppm) |
0 |
900 |
3000 |
9000 |
Body weight of F0 adult males – week 13 (g) |
463.7 (48.93) |
455.2 (34.22) |
455.2 (40.25) |
436.1 (24.83) |
Body weight gain of F0 adult males – week 4-5 (g) |
32.6 (8.98) |
28.9 (8.56) |
24.2 (7.89) |
28.9 (3.78) |
Body weight gain of F0 adult males – week 6-7 (g) |
25.4 (6.17) |
25.4 (6.28) |
23.7 (4.94) |
21.2 (4.31) |
Body weight gain of F0 adult males – week 9-10 (g) |
24.2 (6.00) |
21.6 (6.07) |
18.6 (6.82) |
19.9 (6.17) |
Body weight gain of F0 adult males – week 11-12 (g) |
11.9 (5.40) |
10.7 (6.51) |
12.7 (4.83) |
3.3 (5.70) |
Body weight gain of F0 adult males – week 12-13 (g) |
11.8 (6.26) |
7.4 (6.34) |
8.7 (7.28) |
6.4 (6.09) |
Body weight gain of F0 adult females – week 0-1 (g) |
0.3 (3.08) |
3.4 (3.25) |
1.9 (2.74) |
0.8 (3.67) |
Body weight gain of F0 adult females – week 5-6 (g) |
11.8 (4.01) |
11.0 (4.40) |
12.3 (3.57) |
9.0 (3.20) |
Lactational food consumption F0 – day 7-11 (g/animal/day) |
44.63 (3.859) |
42.93 () |
43.54 (3.796) |
41.45 (3.244) |
Lactational food consumption F0 – day 19-21 (g/animal/day) |
64.41 (5.833) |
64.87 (5.439) |
62.32 (6.595) |
59.81 (8.212) |
No. dead F1 pups - lactational day 4 |
5 |
26 |
12 |
7 |
F1 pup body weight – lactational day 21 (g) |
41.93 (3.950) |
42.50 (4.125) |
39.97 (3.292) |
38.92 (3.996) |
F1 female pup body weight – lactational day 21 (g) |
41.48 (4.151) |
41.75 (4.168) |
39.52 (3.430) |
38.10 (4.063) |
Body weight changes in F1 pups – lactational day 7-14 (g) |
11.91 (1.617) |
12.11 (1.328) |
11.48 (1.381) |
10.56 (1.780) |
Body weight changes in F1 male pups – lactational day 7-14 (g) |
12.00 (1.628) |
12.24 (1.306) |
11.41 (1.708) |
10.71 (1.847) |
Body weight changes in F1 female pups – lactational day 7-14 (g) |
11.81 (1.677) |
12.00 (1.420) |
11.51 (1.536) |
10.35 (1.789) |
Body weight changes in F1 female pups – lactational day 14-21 (g) |
15.86 (1.933) |
15.47 (2.162) |
14.39 (1.744) |
14.24 (2.343) |
Food consumption in F1 females – week 0-1 (g/animal/day) |
20.9 (1.87) |
20.9 (2.00) |
20.7 (2.68) |
19.0 (1.62) |
Food consumption in F1 females – week 1-2 (g/animal/day) |
21.5 (1.45) |
21.2 (2.29) |
21.2 (2.80) |
19.1 (1.90) |
Food consumption in F1 females – week 3-4 (g/animal/day) |
22.0 (2.40) |
21.8 (2.74) |
21.5 (2.98) |
19.6 (1.99) |
Food consumption in F1 females – week 5-6 (g/animal/day) |
20.8 (2.02) |
21.2 (2.60) |
20.6 (2.87) |
19.1 (2.00) |
Food consumption in F1 females – week 7-8 (g/animal/day) |
20.3 (1.84) |
20.3 (2.24) |
20.0 (2.37) |
18.4 (1.99) |
F1 Gestational food consumption – day 0-4 (g/animal/day) |
22.87 (3.172) |
21.93 (2.407) |
21.93 (3.237) |
19.67 (1.703) |
F1 Gestational food consumption – day 4-7 (g/animal/day) |
24.31 (3.047) |
23.63 (3.228) |
23.42 (3.077) |
21.81 (2.072) |
F1 Gestational food consumption – day 0-7 (g/animal/day) |
23.48 (2.972) |
22.44 (2.503) |
22.57 (2.905) |
20.56 (1.760) |
F1 Gestational food consumption – day 7-14 (g/animal/day) |
26.28 (3.268) |
25.25 (3.108) |
24.52 (3.055) |
23.70 (2.565) |
F1 lactational food consumption – day 21-22 (g/animal/day) |
87.77 (15.326) |
79.55 (8.381) |
80.31 (8.272) |
74.01 (9.711) |
F1 lactational food consumption – day 22-23 (g/animal/day) |
91.26 (10.218) |
87.42 (9.649) |
83.36 (8.764) |
81.23 (10.532) |
F1 lactational food consumption – day 23-24 (g/animal/day) |
97.23 (11.339) |
94.59 (9.185) |
90.30 (6.703) |
85.17 (13.188) |
F1 lactational food consumption – day 26-27 (g/animal/day) |
115.86 (11.445) |
114.19 (16.261) |
109.85 (11.689) |
105.38 (15.023) |
F1 lactational food consumption – day 21-28 (g/animal/day) |
102.87 (7.787) |
100.49 (8.471) |
97.47 (6.852) |
94.04 (10.541) |
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 991
- Report date:
- 1991
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 416 (Two-Generation Reproduction Toxicity Study)
- GLP compliance:
- yes (incl. QA statement)
- Limit test:
- no
Test material
- Reference substance name:
- commercial hexane
- IUPAC Name:
- commercial hexane
- Details on test material:
- - Name of test material (as cited in study report): commercial hexane
- Composition of test material, percentage of components: approx. 52% commercial hexane
- Analytical purity: no data
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Breeding Laboratories, Portage, MI
- Age at study initiation: (P) 28 days; (F1) 29-31 days
- Weight at study initiation: (P) Males: 75-100 g; Females: 65-80 g
- Housing: individually except during mating and lactation in stainless steel wire mesh cages, females were housed in plastic cages from gestational day (GD 20) through weaning; animals were identified by ear notches or toe clips
- Diet (e.g. ad libitum): Certified Ground Rodent Diet RMH 3200, ad libitum
- Water (e.g. ad libitum): tap water, ad libitum
- Acclimation period: two weeks
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 68-73 degree F
- Humidity (%): 40-63
- Photoperiod (hrs dark / hrs light): 12 hrs light/12 hrs dark
IN-LIFE DATES: From: Sept. 18, 1989 To: June 16, 1990
Administration / exposure
- Route of administration:
- inhalation: vapour
- Type of inhalation exposure (if applicable):
- whole body
- Details on exposure:
- GENERATION OF TEST ATMOSPHERE / CHAMBER DESCRIPTION
- Exposure apparatus: 900 l glass and stainless steel chambers.
- Method of holding animals in test chamber: cages
- Source and rate of air: 200 l/min
- Method of conditioning air: Test substance was metered from a piston pump into a heated glass evaporator with a temperature of 36-61 degree C. Conditioned air was passed through the evaporator, where it carried the vapor into the exposure chamber.
- Temperature, humidity: monitored every 30 minutes
- Air flow rate: 200 l/min
- Air change rate: 20 min
- Treatment of exhaust air: filtration
TEST ATMOSPHERE
- Brief description of analytical method used: GC with flame ionization detection
- Samples taken from breathing zone: yes, six times per exposure - Details on mating procedure:
- - M/F ratio per cage: 1/1 - If mating failed, females were switched to the male of an unmated pair in the same dose group after 7 days. If mating failed again, they were switched after another 7 days.
- Length of cohabitation: 3 weeks, including during exposure
- Proof of pregnancy: vaginal plug, day 0 - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Samples were taken six times per exposure period and analyzed with GC-FID. Distribution of test substance was evaluated by sampling nine different areas of the exposure chamber.
- Duration of treatment / exposure:
- 10 weeks pre-breeding, 3 weeks during breeding
Females continued to be exposed through GD 19. Exposure was resumed on postnatal day 5, and continued through weaning.
The F1 generation was treated similarly, but pre-breeding exposure was 8 weeks. - Frequency of treatment:
- 6 hrs/day, 5 days/week
- Details on study schedule:
- - F1 parental animals not mated until 9 weeks after selected from the F1 litters.
- Selection of parents from F1 generation when pups were 28 days of age.
- Age at mating of the mated animals in the study: 13-16 weeks
Doses / concentrationsopen allclose all
- Remarks:
- Doses / Concentrations:
0, 900, 3000, 9000 ppm
Basis:
nominal conc.
- Remarks:
- Doses / Concentrations:
892, 2995, 9019 ppm
Basis:
analytical conc.
- No. of animals per sex per dose:
- 25 per sex per dose
- Control animals:
- yes, sham-exposed
Examinations
- Parental animals: Observations and examinations:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: twice daily
- Cage side observations: mortality, toxicity, littering, mating
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: once daily
BODY WEIGHT: Yes
- Time schedule for examinations: weekly
FOOD CONSUMPTION:
- Food consumption: Yes, food consumption of pregnant females was measured in 3-4 day intervals, and through postnatal day 28. - Litter observations:
- STANDARDISATION OF LITTERS
Parents of the F2 generation were selected on day 28 postpartum, at least one pup per litter was selected, with a second pup selected only if all litters were already represented. The F2 generation was standardized on day 4 postpartum.
PARAMETERS EXAMINED
The following parameters were examined in F1 and F2 offspring:
number and sex of pups, stillbirths, live births, postnatal mortality, presence of gross anomalies, weight gain, physical abnormalities
GROSS EXAMINATION OF DEAD PUPS:
yes, for external abnormalities - Postmortem examinations (parental animals):
- SACRIFICE
- Male animals: All surviving animals after parturition of the first litter
- Maternal animals: All surviving animals day after weaning.
GROSS NECROPSY
- Gross necropsy consisted of external surfaces, orifices, cranial cavity, carcass, brain, spinal cord, thoracic cavity, abdominal cavity, pelvic cavity, cervical tissues and organs
HISTOPATHOLOGY / ORGAN WEIGHTS
Tissues from 25 male and females from the high dose and control groups were examined including testes of males failing to mate. - Postmortem examinations (offspring):
- SACRIFICE
- The F1 offspring not selected as parental animals and all F2 offspring were sacrificed at 28 days of age.
- These animals were subjected to postmortem examinations as follows: stillborn and pups dying during lactation, culled pups
GROSS NECROPSY
- Gross necropsy consisted of external examinations. - Statistics:
- Quantitative continuous variables were compared by use of Levene's test for equal variance, analysis of variance, and t-tests. Significance for t-tests were corrected by the Bonferroni method. Nonparametric data was evaluated using the Kruskal-Wallis test, followed by the Mann-Whitney test. Indices were compared using Fisher's exact test. 0.05 was used as the criteria for statistical significance.
- Reproductive indices:
- mating index, fertility index, gestational index, live birth index,
- Offspring viability indices:
- 4-day survival index, 7-day survival index, 14-day survival index, 21-day survival index, lactation index
Results and discussion
Results: P0 (first parental generation)
Details on results (P0)
CLINICAL SIGNS AND MORTALITY (PARENTAL ANIMALS)
No treatment related effects observed.
BODY WEIGHT AND FOOD CONSUMPTION (PARENTAL ANIMALS)
There were no treatment related effects on food consumption. Males in the 9000 ppm group had reduced body weight during week 13. Body weight gains in this group were reduced during weeks 7, 11-12, and 12-13. Males in the 3000 ppm group had reduced body weight gain in weeks 4-5, and reduced weight in weeks 9-10. Females weight gains were reduced in the 9000 ppm group in weeks 5-6.
REPRODUCTIVE PERFORMANCE (PARENTAL ANIMALS)
Lactational food consumption was significantly reduced during days 7-11, and days 19-21 in the 9000 ppm group. No other reproductive parameters differed significantly from controls.
GROSS PATHOLOGY (PARENTAL ANIMALS)
No treatment related abnormalities were seen.
HISTOPATHOLOGY (PARENTAL ANIMALS)
Hyaline droplet nephropathy and tubular basophilia were seen in the 9000 ppm males.
F1 GENERATION
CLINICAL SIGNS AND MORTALITY (PARENTAL ANIMALS)
No treatment related effects were observed. One female in the 900 ppm group died on day 83 due to prolonged delivery.
BODY WEIGHT AND FOOD CONSUMPTION (PARENTAL ANIMALS)
Body weights of 9000 ppm males were significantly reduced throughout the exposure period. Weight gain was reduced in this group during the weeks 9-10, and 10-11. Females in the 9000 ppm group had reduced body weight during the first 3 weeks of pre-breeding exposure.
REPRODUCTIVE PERFORMANCE (PARENTAL ANIMALS)
In the 9000 ppm group, food consumption was reduced on gestational days 0-4, and 4-7, and gestational intervals 0-7, and 7-14. This group also had reduced food consumption during lactational days 21-24, 26-27, 21, and 28. In the 3000 ppm group, food consumption was reduced during lactational days 22-23, and in the 900 ppm group during days lactational days 21-22.
GROSS PATHOLOGY (PARENTAL ANIMALS)
No treatment related abnormalities were seen.
HISTOPATHOLOGY (PARENTAL ANIMALS)
Hyaline droplet nephropathy and tubular basophilia were seen in the 9000 ppm males.
Effect levels (P0)
- Key result
- Dose descriptor:
- NOAEC
- Effect level:
- 31 680 mg/m³ air (nominal)
- Sex:
- male/female
- Basis for effect level:
- other: The value was re-calculated from the nominal dose of 9000 ppm.
- Remarks on result:
- other: Generation: reproductive toxicity
Results: F1 generation
Details on results (F1)
VIABILITY (OFFSPRING)
The number of dead pups was increased in the 900 ppm exposure group, however, as this was not seen at higher doses, it was not considered treatment related.
BODY WEIGHT (OFFSPRING)
The body weight of pups in the 9000 ppm group were reduced beginning on lactational day 14. Body weight gains in this group were reduced during lactational days 14-21 for females, and lactational days 7-14 for all pups.
GROSS PATHOLOGY (OFFSPRING)
No treatment related effects were noted.
F2 GENERATION
VIABILITY (OFFSPRING)
Viability was unaffected by exposure.
BODY WEIGHT (OFFSPRING)
The body weight of pups in the 9000 ppm group were reduced from lactational day 7-28. Body weight gains in this group were reduced during lactational days 14-21 for females, and lactational days 7-14 for all pups. There were significantly reduced body weight gains in pups in the 9000 ppm group during lactational days 4-7, and 7-14, and slightly reduced weight gains on lactational days 14-21.
GROSS PATHOLOGY (OFFSPRING)
No treatment related effects were noted.
Effect levels (F1)
open allclose all
- Key result
- Dose descriptor:
- NOAEC
- Effect level:
- 10 560 mg/m³ air (nominal)
- Sex:
- male/female
- Basis for effect level:
- other: reduced body weight. The value was re-calculated from the nominal dose of 3000 ppm
- Remarks on result:
- other: Generation F1, F2
- Key result
- Dose descriptor:
- LOAEC
- Effect level:
- 31 680 mg/m³ air (nominal)
- Sex:
- male/female
- Basis for effect level:
- other: reduced body weight. The value was recalculated from the nominal dose of 9000 ppm
- Remarks on result:
- other: Generation F1, F2
Overall reproductive toxicity
- Key result
- Reproductive effects observed:
- not specified
Any other information on results incl. tables
Significant Results of Reproductive Toxicity Study on Rats
Concentration (ppm) |
0 |
900 |
3000 |
9000 |
Body weight of F0 adult males – week 13 (g) |
463.7 (48.93) |
455.2 (34.22) |
455.2 (40.25) |
436.1 (24.83) |
Body weight gain of F0 adult males – week 4-5 (g) |
32.6 (8.98) |
28.9 (8.56) |
24.2 (7.89) |
28.9 (3.78) |
Body weight gain of F0 adult males – week 6-7 (g) |
25.4 (6.17) |
25.4 (6.28) |
23.7 (4.94) |
21.2 (4.31) |
Body weight gain of F0 adult males – week 9-10 (g) |
24.2 (6.00) |
21.6 (6.07) |
18.6 (6.82) |
19.9 (6.17) |
Body weight gain of F0 adult males – week 11-12 (g) |
11.9 (5.40) |
10.7 (6.51) |
12.7 (4.83) |
3.3 (5.70) |
Body weight gain of F0 adult males – week 12-13 (g) |
11.8 (6.26) |
7.4 (6.34) |
8.7 (7.28) |
6.4 (6.09) |
Body weight gain of F0 adult females – week 0-1 (g) |
0.3 (3.08) |
3.4 (3.25) |
1.9 (2.74) |
0.8 (3.67) |
Body weight gain of F0 adult females – week 5-6 (g) |
11.8 (4.01) |
11.0 (4.40) |
12.3 (3.57) |
9.0 (3.20) |
Lactational food consumption F0 – day 7-11 (g/animal/day) |
44.63 (3.859) |
42.93 () |
43.54 (3.796) |
41.45 (3.244) |
Lactational food consumption F0 – day 19-21 (g/animal/day) |
64.41 (5.833) |
64.87 (5.439) |
62.32 (6.595) |
59.81 (8.212) |
No. dead F1 pups - lactational day 4 |
5 |
26 |
12 |
7 |
F1 pup body weight – lactational day 21 (g) |
41.93 (3.950) |
42.50 (4.125) |
39.97 (3.292) |
38.92 (3.996) |
F1 female pup body weight – lactational day 21 (g) |
41.48 (4.151) |
41.75 (4.168) |
39.52 (3.430) |
38.10 (4.063) |
Body weight changes in F1 pups – lactational day 7-14 (g) |
11.91 (1.617) |
12.11 (1.328) |
11.48 (1.381) |
10.56 (1.780) |
Body weight changes in F1 male pups – lactational day 7-14 (g) |
12.00 (1.628) |
12.24 (1.306) |
11.41 (1.708) |
10.71 (1.847) |
Body weight changes in F1 female pups – lactational day 7-14 (g) |
11.81 (1.677) |
12.00 (1.420) |
11.51 (1.536) |
10.35 (1.789) |
Body weight changes in F1 female pups – lactational day 14-21 (g) |
15.86 (1.933) |
15.47 (2.162) |
14.39 (1.744) |
14.24 (2.343) |
Food consumption in F1 females – week 0-1 (g/animal/day) |
20.9 (1.87) |
20.9 (2.00) |
20.7 (2.68) |
19.0 (1.62) |
Food consumption in F1 females – week 1-2 (g/animal/day) |
21.5 (1.45) |
21.2 (2.29) |
21.2 (2.80) |
19.1 (1.90) |
Food consumption in F1 females – week 3-4 (g/animal/day) |
22.0 (2.40) |
21.8 (2.74) |
21.5 (2.98) |
19.6 (1.99) |
Food consumption in F1 females – week 5-6 (g/animal/day) |
20.8 (2.02) |
21.2 (2.60) |
20.6 (2.87) |
19.1 (2.00) |
Food consumption in F1 females – week 7-8 (g/animal/day) |
20.3 (1.84) |
20.3 (2.24) |
20.0 (2.37) |
18.4 (1.99) |
F1 Gestational food consumption – day 0-4 (g/animal/day) |
22.87 (3.172) |
21.93 (2.407) |
21.93 (3.237) |
19.67 (1.703) |
F1 Gestational food consumption – day 4-7 (g/animal/day) |
24.31 (3.047) |
23.63 (3.228) |
23.42 (3.077) |
21.81 (2.072) |
F1 Gestational food consumption – day 0-7 (g/animal/day) |
23.48 (2.972) |
22.44 (2.503) |
22.57 (2.905) |
20.56 (1.760) |
F1 Gestational food consumption – day 7-14 (g/animal/day) |
26.28 (3.268) |
25.25 (3.108) |
24.52 (3.055) |
23.70 (2.565) |
F1 lactational food consumption – day 21-22 (g/animal/day) |
87.77 (15.326) |
79.55 (8.381) |
80.31 (8.272) |
74.01 (9.711) |
F1 lactational food consumption – day 22-23 (g/animal/day) |
91.26 (10.218) |
87.42 (9.649) |
83.36 (8.764) |
81.23 (10.532) |
F1 lactational food consumption – day 23-24 (g/animal/day) |
97.23 (11.339) |
94.59 (9.185) |
90.30 (6.703) |
85.17 (13.188) |
F1 lactational food consumption – day 26-27 (g/animal/day) |
115.86 (11.445) |
114.19 (16.261) |
109.85 (11.689) |
105.38 (15.023) |
F1 lactational food consumption – day 21-28 (g/animal/day) |
102.87 (7.787) |
100.49 (8.471) |
97.47 (6.852) |
94.04 (10.541) |
Applicant's summary and conclusion
- Conclusions:
- The NOAEC for both male and female rats (adults and offspring) was 3000 ppm. The LOAEC for these groups was 9000 ppm based on reduced body weight. There were no adverse effects on reproduction, therefore the NOAEC for reproduction is 9000 ppm.
- Executive summary:
The purpose of this study was to determine the effect of commercial hexane on reproduction in rats. Groups of 25 male and 25 female rats were exposed to nominal concentrations of 0, 900, 3000, or 9000 ppm of test substance for 10 weeks pre-breeding, 3 weeks during breeding, and postnatal days 4 -28. After weaning, pups were selected to be parents for the F2 generations, and treated similarly to their parents, except their pre-breeding exposure was 8 weeks. During exposure, animals were monitored for mortality, clinical signs, food consumption, and body weight. Offspring were examined for body weight, survival, and viability. Both parents and offspring were sacrificed and examined for gross abnormalities, and in the case of adults histopathology. Reproductive parameters were similar in exposure groups and control groups. There was reduced body weight in the F1 and F2 generation in both sexes in the 9000 ppm exposure group in both adults and offspring. The NOAEC is therefore 3000 ppm, and the LOAEC is 9000 ppm. Since there were no adverse effects in offspring without adverse maternal effects, the NOAEC for reproduction is 9000 ppm.
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