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EC number: 201-291-9 | CAS number: 80-56-8
- 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
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- Endpoint summary
- Stability
- Biodegradation
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- 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
Repeated dose toxicity: inhalation
Administrative data
- Endpoint:
- sub-chronic toxicity: inhalation
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 14 weeks in 2005
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study with acceptable restrictions
- Remarks:
- Whole body exposure, and fixation of cauda tissue at 65°C
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 2 016
- Report date:
- 2016
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 413 (Subchronic Inhalation Toxicity: 90-Day Study)
- Deviations:
- yes
- Remarks:
- no data on food consumption, no ophthalmological examination, some organ weights were not recorded (Adrenals, brain, heart, Ovaries, thyroids, Uterus). Animals weighed weekly and not twice weekly
- Principles of method if other than guideline:
- Not applicable
- GLP compliance:
- yes
- Remarks:
- in compliance with Food and Drug Administration Good Laboratory Practice Regulations (21 CFR, Part 58).
- Limit test:
- no
Test material
- Reference substance name:
- Pin-2(3)-ene
- EC Number:
- 201-291-9
- EC Name:
- Pin-2(3)-ene
- Cas Number:
- 80-56-8
- Molecular formula:
- C10H16
- IUPAC Name:
- 2,6,6-trimethylbicyclo[3.1.1]hept-2-ene
- Test material form:
- liquid
Constituent 1
- Specific details on test material used for the study:
- - lot 4KB705 supplied from Millennium Specialty Chemicals (Jacksonville, FL), purity 96%
- water content of 27 ppm (Karl Fischer titration)
- 69% (+)-α-pinene and 31% (–)-α-pinene (GC/FID)
- Identified impurities: camphene (1.77%) and β-pinene (1.73%) identified by GC/FID, and tricyclene (0.51%) identified by GC/MS.
Test animals
- Species:
- mouse
- Strain:
- B6C3F1
- Details on species / strain selection:
- Male and female B6C3F1/N mice were obtained from the NTP colony maintained at Taconic Farms, Inc. (Germantown, NY),
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- - Source: Male and female B6C3F1/N mice were obtained from the NTP colony maintained at Taconic Farms, Inc. (Germantown, NY),
- Age at the study initiate: 5 to 6 weeks
- Animals were quarantined for 12 days before the study and after, assigned at random to treatment groups.
- Housing: Mice were housed individually in stainless steel, wire bottom cages (LabProducts, Inc., Seaford, DE); changed weekly.
- Diet: NTP-2000 irradiated wafers (Zeigler Brothers, Inc., Gardners, PA), available ad libitum (except during exposure periods); changed weekly.
Water: Tap water (Richland, WA, municipal supply) via automatic watering system (Edstrom Industries, Waterford, WI); available ad libitum
- Chamber environment:
Temperature: 72° ± 3° F
Relative humidity: 50% ± 15%
Room fluorescent light: 12 hours/day
Chamber air changes: 15 ± 2/hour
Administration / exposure
- Route of administration:
- inhalation: vapour
- Type of inhalation exposure:
- whole body
- Vehicle:
- not specified
- Remarks on MMAD:
- MMAD / GSD: No data
- Details on inhalation exposure:
- No data
- Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Chamber and room concentrations of α-pinene were monitored by an on-line gas chromatograph. Samples were drawn from each exposure chamber approximately every 20 minutes during each 6-hour exposure period.
Average concentration measured were 24.9 ± 1.1ppm for the 25 ppm group, 49.8 ± 0.8 ppm for the 50 ppm group, 99.6 ± 1.4 ppm for the 100 ppm group, 200 ± 4 ppm for the 200 ppm group, 401 ± 7 ppm for the 400 ppm group. - Duration of treatment / exposure:
- 6 hours plus T90 (10 minutes) per day, 5 days per week, for 14 weeks
- Frequency of treatment:
- Five times per week, weekdays only
Doses / concentrationsopen allclose all
- Dose / conc.:
- 25 ppm
- Remarks:
- nominal conc.
- Dose / conc.:
- 50 ppm
- Remarks:
- nominal conc.
- Dose / conc.:
- 100 ppm
- Remarks:
- nominal conc.
- Dose / conc.:
- 200 ppm
- Remarks:
- nominal conc.
- Dose / conc.:
- 400 ppm
- Remarks:
- nominal conc.
- No. of animals per sex per dose:
- 10
- Control animals:
- yes
- Details on study design:
- Before the studies began, five male and five female mice were randomly selected for parasite evaluation and gross observation for evidence of disease.
- Core study animals were weighed initially, and body weights and clinical findings were recorded on day 8, weekly thereafter, and at the end of the studies.
- Serologic analyses were performed on five male and five female sentinel mice at 1 week and at the end of the studies using the protocols of the NTP Sentinel Animal Program
- Animals were anesthetized with carbon dioxide, and blood was collected from the retroorbital plexus of clinical pathology rats on days 4 and 23 and from core study mice at the end of the studies for hematology analyses. - Positive control:
- No
Examinations
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes for moribundity and death
- Time schedule: twice daily, at least 6 hours apart (before 10:00 AM and after 2:00 PM)
DETAILED CLINICAL OBSERVATIONS: Yes
Clinical findings were recorded on day 7 (female rats) and day 8 (male rats), weekly thereafter, and at the end of the studies.
BODY WEIGHT: Yes
- Time schedule for examinations: Animals were weighed initially on Day 1, on days 7 (female rats) and days 8 (male rats), weekly thereafter, and at the end of the studies;
FOOD CONSUMPTION: No
FOOD EFFICIENCY: No
WATER CONSUMPTION: No
OPHTHALMOSCOPIC EXAMINATION: No
HAEMATOLOGY: Yes, collected from the retroorbital plexuscof clinical pathology rats at the end of the study.
- Parameters examined: hematocrit; packed cell volume; hemoglobin; erythrocyte, reticulocyte, and platelet counts; Howell-Jolly bodies (mice); mean cell volume; mean cell hemoglobin; mean cell hemoglobin concentration; and leukocyte counts and differentials.
CLINICAL CHEMISTRY: Yes, collected from the retroorbital plexuscof clinical pathology rats at the end of the study.
- Parameters examined: urea nitrogen, creatinine, total protein, albumin, globulin, alanine aminotransferase, alkaline phosphatase, creatine kinase, sorbitol dehydrogenase, and bile salts.
URINALYSIS: No
NEUROBEHAVIOURAL EXAMINATION: No - Sacrifice and pathology:
- METHOD OF KILL: Carbon dioxide asphyxiation
GROSS PATHOLOGY: : Yes
Heart, right kidney, liver, lung, spleen, right testis, and thymus were weighed. Tissues for microscopic examination were fixed and preserved in 10% neutral buffered formalin, processed and trimmed, embedded in paraffin, sectioned to a thickness of 4 to 6 μm, and stained with hematoxylin and eosin.
HISTOPATHOLOGY: Yes, complete histopathologic examinations were performed by the study laboratory pathologist on all chamber control and 400 ppm animals and 200 ppm female rats.
In addition to gross lesions and tissue masses, the following tissues were examined:
adrenal gland, bone, brain, clitoral gland, esophagus, eyes, Harderian gland, gallbladder, heart and aorta, large intestine (cecum, colon, rectum), small intestine (duodenum, jejunum, ileum), kidney, larynx, liver, lung and mainstem bronchi, lymph nodes (mandibular, mesenteric, bronchial, mediastinal), mammary gland, nose, ovary, pancreas, parathyroid gland, pituitary gland, preputial gland, prostate gland, salivary gland, skin, spleen, stomach (forestomach and glandular), testis with epididymis and seminal vesicles, thymus, thyroid gland, trachea, urinary bladder, and uterus. The liver of male rats and the kidney of rats were examined in the remaining groups. - Other examinations:
- SPERM MOTILITY AND VAGINAL CYTOLOGY: At the end of the study, sperm samples were collected for sperm motility evaluations. Sperm heads per testis and per gram testis, spermatid counts, and epididymal spermatozoal motility and concentration. were evaluated. The left cauda, left epididymis, and left testis were weighed. The numbers of motile and nonmotile spermatozoa were counted for five fields per slide by two observers. Sperm density was then determined microscopically with the aid of a hemacytometer
Vaginal samples were collected for up to 12 consecutive days prior to the end of the study for vaginal cytology evaluations. The percentage of time spent in the various estrous cycle stages and estrous cycle length were evaluated. - Statistics:
- Kaplan-Meier used for probability of survival. Statistical analyses used for possible dose-related effect on survival was Cox (Cox D.R. (1972) Regression models and life tables. J.R. Stat. Soc. B34: 187-220.) for testing two groups for equality; and Tarone’s (Tarone R.E. (1975) Tests for trend in life table analysis. Biometrika 62; 679-682) life table test for a dose-related trend.
Fisher exact test (Gart et al., 1979) was used to determine significance.
Results and discussion
Results of examinations
- Clinical signs:
- no effects observed
- Mortality:
- no mortality observed
- Description (incidence):
- no mortality
- Body weight and weight changes:
- no effects observed
- Description (incidence and severity):
- (See table 1 for raw data)
- Food consumption and compound intake (if feeding study):
- not examined
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- effects observed, non-treatment-related
- Description (incidence and severity):
- Changes were observed but were either considered as secondary treatment-associated stress effects or not considered as toxicologically relevant. (See table 4)
- Clinical biochemistry findings:
- not examined
- Urinalysis findings:
- not examined
- Behaviour (functional findings):
- not examined
- Immunological findings:
- not examined
- Organ weight findings including organ / body weight ratios:
- effects observed, treatment-related
- Description (incidence and severity):
- Changes were observed but no gross or microscopic lesions were associated with these organ weight findings. (See table 2)
- Gross pathological findings:
- not specified
- Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Description (incidence and severity):
- Hyperplasia of the transitional epithelium of the urinary bladder, were observed from 100 ppm in males and females. However, there was no evidence of histopathological changes to the clitoris, ovaries, uterus, epididymis, preputial gland, seminal vesicles, and testes in any groups of animals. (See table 3)
- Histopathological findings: neoplastic:
- not specified
- Other effects:
- effects observed, treatment-related
- Description (incidence and severity):
- There were significantly decreased sperm count per mg cauda in males treated at 200 and 400 ppm and in cauda sperm counts in 100, 200, and 400 ppm groups (See table 5)
However, the relevance of these effects can be questioned: first, the heat fixation at 65°C of caudae samples for sperm counts may have altered the integrity of the samples; secondly, these changes in sperm levels were not corroborated by other findings such as histopathological changes in other reproductive organs/tissues or other sperm parameters (motility, spermatid counts, etc.). Also, these decreases might be secondary to stress induced by hyperplasia of bladder epithelium at the 3 highest doses. - Details on results:
- MORTALITY
All mice survived until the terminal sacrifice.
CLINICAL EXAMINATION
There were no treatment-related clinical signs.
BODY WEIGHT AND WEIGHT GAIN
Body weight gain was comparable for all test animals when compared to controls.
CLINICAL CHEMISTRY
No data available.
ORGAN WEIGHTS
Absolute liver weights were increased for both sexes at the 400 ppm and relative and absolute liver weights were increased for both sexes at 200 ppm and 400 ppm, and for female only at 100 ppm. The 400 ppm male group showed decreased absolute and relative thymus weight. The basolute kidney weights for 200 and 400 ppm males were significantly less than those of the control group. No gross or microscopic lesions were associated with these organ weight findings.
HISTOPATHOLOGY: NON-NEOPLASTIC
Histopathological examination of male and female mice exposed to atmospheres of ≥100 ppm of α-pinene revealed evidence of hyperplasia of the transitional epithelium of the urinary bladder. However, there was no evidence of histopathological changes to the clitoris, ovaries, uterus, epididymis, preputial gland, seminal vesicles, and testes any of the control or test groups of animals.
HEMATOLOGY:
At the end of the study, there were small but statistically significant decreases in erythrocyte counts in 200 and 400 ppm females and in the hemoglobin concentration and the hematocrit value in 400 ppm females compared to concurrent controls. Decreases in erythrocyte count and hematocrit value also occurred in 400 ppm males.
Leukocyte and lymphocyte counts were significantly decreased in 400 ppm males. The leukocyte changes likely represent a secondary treatment-associated stress effect. The exact mechanism for the mild decreases in the erythron are not known. Other significant changes in hematology parameters were not toxicologically relevant.
SPERM MOTILITY AND VAGINAL CYTOLOGY:
There were significantly decreased numbers of sperm per mg cauda in 200 and 400 ppm males and cauda sperm in 100, 200, and 400 ppm males. There were no changes in the proportion of regularly cycling females, estrous cycle length, or percentage of time spent in the individual stages of the estrous cycle of female mice at any exposure concentration and there were no ovarian histopathologic findings.
Therefore, α-pinene exposure via inhalation exhibits the potential to be a reproductive toxicant in male mice, but not in female mice
Effect levels
open allclose all
- Key result
- Dose descriptor:
- LOAEC
- Effect level:
- 100 ppm
- Based on:
- test mat.
- Sex:
- male
- Basis for effect level:
- other: significantly decreased sperm count per mg cauda in males treated at 200 and 400 ppm and in cauda sperm counts in 100, 200, and 400 ppm groups
- Dose descriptor:
- NOAEC
- Effect level:
- 50 ppm
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- histopathology: non-neoplastic
Target system / organ toxicity
open allclose all
- Key result
- Critical effects observed:
- yes
- Lowest effective dose / conc.:
- 100 ppm
- System:
- urinary
- Organ:
- bladder
- Treatment related:
- yes
- Dose response relationship:
- yes
- Relevant for humans:
- not specified
- Critical effects observed:
- yes
- Lowest effective dose / conc.:
- 100 ppm
- System:
- male reproductive system
- Organ:
- cauda epididymis
- Treatment related:
- yes
- Dose response relationship:
- yes
- Relevant for humans:
- yes
Any other information on results incl. tables
Table 1: Mean of body weights and body weight gainsa:
Concentration(ppm) | Survivalb | Initial Body Weight (g) | Final Body Weight (g) | Change in Body Weight(g) | Final Weight Relative to Controls (%) | |
Male | 0 | 10/10 | 22.9 ± 0.2 | 37.1 ± 0.6 | 14.3 ± 0.6 | |
25 | 10/10 | 23.0 ± 0.3 | 36.9 ± 0.7 | 13.9 ± 0.8 | 99 | |
50 | 10/10 | 22.7 ± 0.3 | 38.3 ± 0.9 | 15.6 ± 0.8 | 103 | |
100 | 10/10 | 22.5 ± 0.2 | 35.9 ± 0.7 | 13.4 ± 0.7 | 97 | |
200 | 10/10 | 22.8 ± 0.3 | 35.5 ± 1.0 | 12.7 ± 0.9 | 96 | |
400 | 10/10 | 22.8 ± 0.2 | 36.2 ± 0.5 | 13.5 ± 0.4 | 98 | |
Female | 0 | 10/10 | 19.5 ± 0.4 | 31.5 ± 0.6 | 12.0 ± 0.5 | |
25 | 10/10 | 19.6 ± 0.4 | 30.3 ± 0.6 | 10.8 ± 0.7 | 96 | |
50 | 10/10 | 19.7 ± 0.3 | 32.7 ± 0.7 | 12.9 ± 0.7 | 104 | |
100 | 10/10 | 19.7 ± 0.4 | 31.5 ± 1.1 | 11.8 ± 0.9 | 100 | |
200 | 10/10 | 19.3 ± 0.3 | 30.7 ± 0.6 | 11.4 ± 0.6 | 97 | |
400 | 10/10 | 19.4 ± 0.3 | 30.6 ± 0.5 | 11.2 ± 0.4 | 97 |
a Weights and weight changes are given as mean ± standard error.
b Number of animals surviving at 14 weeks/number initially in group
Table 2: Mean of absolute and relative organ weight
Chamber control | 25 ppm | 50 ppm | 100 ppm | 200 ppm | 400 ppm | |
Male | ||||||
n | 10 | 10 | 10 | 10 | 10 | 10 |
Necropsy body wt | 37.1 ± 0.6 | 36.9 ± 0.7 | 38.3 ± 0.9 | 35.9 ± 0.7 | 35.5 ± 1.0 | 36.2 ± 0.5 |
R Kidney absolute | 0.330 ± 0.006 | 0.318 ± 0.009 | 0.336 ± 0.010 | 0.309 ± 0.008 | 0.295 ± 0.006* | 0.307 ± 0.007* |
R kidney relative | 8.903 ± 0.167 | 8.629 ± 0.208 | 8.793 ± 0.267 | 8.617 ± 0.205 | 8.348 ± 0.145 | 8.469 ± 0.155 |
Liver absolute | 1.617 ± 0.022 | 1.589 ± 0.028 | 1.702 ± 0.040 | 1.637 ± 0.024 | 1.660 ± 0.043 | 1.957 ± 0.057** |
Liver relative | 43.671 ± 0.880 | 43.123 ± 0.458 | 44.487 ± 0.806 | 45.651 ± 0.678 | 46.903 ± 0.750* | 54.009 ± 1.465** |
Thymus absolute | 0.066 ± 0.004 | 0.063 ± 0.004 | 0.067 ± 0.003 | 0.057 ± 0.001 | 0.062 ± 0.004 | 0.051 ± 0.003** |
Thymus relative | 1.777 ± 0.081 | 1.699 ± 0.090 | 1.742 ± 0.063 | 1.591 ± 0.052 | 1.739 ± 0.115 | 1.397 ± 0.081** |
Female | ||||||
n | 10 | 10 | 10 | 10 | 10 | 10 |
Necropsy body wt | 31.5 ± 0.6 | 30.3 ± 0.6 | 32.7 ± 0.7 | 31.5 ± 1.1 | 30.7 ± 0.6 | 30.6 ± 0.5 |
Liver absolute | 1.466 ± 0.041 | 1.475 ± 0.053 | 1.442 ± 0.036 | 1.548 ± 0.053 | 1.587 ± 0.037 | 1.730 ± 0.032** |
Liver relative | 46.542 ± 0.988 | 48.567 ± 1.239 | 44.214 ± 0.880 | 49.280 ± 0.672* | 51.728 ± 0.795** | 56.511 ± 0.705** |
aOrgan weights (absolute weights) and body weights are given in grams; organ-weight-to-body-weight ratios (relative weights) are given as mg organ weight/g body weight (mean ± standard error).
* Significantly different (P≤0.05) from the chamber control group by Williams’ or Dunnett’s test
** Significantly different (P≤0.01) from the chamber control group by Williams’ or Dunnett’s test
Table 3: Incidence of Non neoplastic lesions of the urinary bladder
Sexe | Treatment concentration (ppm) | 0 (control group) | 25 | 50 | 100 | 200 | 400 |
Male | Number Examined Microscopically | 10 | 10 | 10 | 10 | 10 | 10 |
Male | Transitional Epithelium, Hyperplasiaa | 0 | 0 | 0 | 7** (1.0)b | 10** (2.0)b | 10** (2.5)b |
Female | Number Examined Microscopically | 10 | 10 | 10 | 10 | 10 | 10 |
Female | Transitional Epithelium, Hyperplasiaa | 0 | 0 | 0 | 6** (1.0)b | 10** (1.6)b | 10** (2.2)b |
a Number of animals with lesion
b Average severity grade of lesions in affected animals: 1=minimal, 2=mild, 3=moderate, 4=marked
Table 4: Hematology data
Treatment concentration (ppm) | 0 (control group) | 25 | 50 | 100 | 200 | 400 |
Male | ||||||
Hematocrit (spun) (%) | 51.3 ± 0.3 | 50.5 ± 0.4 | 50.1 ± 0.3 | 51.1 ± 0.3 | 50.9 ± 0.4 | 49.8 ± 0.3* |
Hemoglobin (g/dL) | 16.0 ± 0.1 | 16.0 ± 0.1 | 15.7 ± 0.1 | 16.0 ± 0.0 | 16.1 ± 0.1 | 15.7 ± 0.1 |
Erythrocytes (106/µL) | 10.51 ± 0.06 | 10.47 ± 0.06 | 10.23 ± 0.09 | 10.52 ± 0.04 | 10.55 ± 0.08 | 10.10 ± 0.07** |
Reticulocytes(103/µL)Nucleated erythrocytes/100 leukocytes | 223.7 ± 19.4 0.00 ± 0.00 | 200.3 ± 14.9 0.00 ± 0.00 | 193.9 ± 16.4 0.00 ± 0.00 | 205.2 ± 13.0 0.00 ± 0.00 | 214.3 ± 16.4 0.00 ± 0.00 | 202.2 ± 15.9 0.00 ± 0.00 |
Mean cell volume (fL) | 49.3 ± 0.3 | 49.2 ± 0.2 | 49.6 ± 0.2 | 49.4 ± 0.2 | 49.6 ± 0.2 | 50.6 ± 0.2** |
Mean cell hemoglobin (pg)Mean cell hemoglobin concentration (g/dL) | 15.3 ± 0.1 31.0 ± 0.2 | 15.2 ± 0.1 31.0 ± 0.1 | 15.4 ± 0.1 31.0 ± 0.1 | 15.2 ± 0.0 30.8 ± 0.2 | 15.2 ± 0.0 30.7 ± 0.1 | 15.6 ± 0.1* 30.8 ± 0.1 |
Leukocytes (103/µL) | 3.10 ± 0.40 | 2.94 ± 0.43 | 2.03 ± 0.26 | 2.47 ± 0.15 | 2.31 ± 0.26 | 1.87 ± 0.17* |
Lymphocytes (103/µL) | 2.60 ± 0.34 | 2.41 ± 0.39 | 1.73 ± 0.23 | 2.03 ± 0.13 | 1.93 ± 0.22 | 1.48 ± 0.14* |
Female | ||||||
Hematocrit (spun) (%) | 49.6 ± 0.3 | 50.1 ± 0.4 | 49.4 ± 0.5 | 50.1 ± 0.3 | 48.9 ± 0.3 | 48.3 ± 0.3* |
Hemoglobin (g/dL) | 15.8 ± 0.1 | 16.0 ± 0.1 | 15.7 ± 0.2 | 15.9 ± 0.1 | 15.5 ± 0.1 | 15.5 ± 0.1* |
Erythrocytes (106/µL) | 10.21 ± 0.05 | 10.26 ± 0.06 | 10.10 ± 0.11 | 10.14 ± 0.06 | 9.96 ± 0.09* | 9.85 ± 0.08** |
Reticulocytes(103/µL)Nucleated erythrocytes/100 leukocytes | 269.5 ± 15.4 0.00 ± 0.00 | 248.9 ± 14.9 0.00 ± 0.00 | 251.9 ± 16.5 0.00 ± 0.00 | 282.5 ± 18.3 0.00 ± 0.00 | 240.1 ± 20.8 0.00 ± 0.00 | 251.2 ± 15.3 0.00 ± 0.00 |
Mean cell volume (fL) | 49.3 ± 0.2 | 49.7 ± 0.2 | 49.5 ± 0.3 | 50.1 ± 0.2* | 49.7 ± 0.2 | 49.7 ± 0.2 |
Mean cell hemoglobin (pg)Mean cell hemoglobin concentration (g/dL) | 15.5 ± 0.1 31.5 ± 0.2 | 15.6 ± 0.1 31.4 ± 0.1 | 15.5 ± 0.1 31.4 ± 0.2 | 15.6 ± 0.1 31.1 ± 0.1 | 15.6 ± 0.1 31.4 ± 0.1 | 15.7 ± 0.1 31.6 ± 0.1 |
Leukocytes (103/µL) | 3.65 ± 0.35 | 3.10 ± 0.27 | 3.34 ± 0.32 | 2.80 ± 0.29 | 3.11 ± 0.32 | 3.16 ± 0.34 |
Lymphocytes (103/µL) | 3.09 ± 0.30 | 2.65 ± 0.23 | 2.78 ± 0.30 | 2.39 ± 0.25 | 2.60 ± 0.26 | 2.66 ± 0.27 |
* Significantly different (P≤0.05) from the chamber control group by Dunn’s or Shirley’s test
** P≤0.01
Data are presented as mean ± standard error. Statistical tests were performed on unrounded data.
Table 5 Mean of epididymal spermatozoal measurements
Chamber control | 100 ppm | 200 ppm | 400 ppm | |
n | 10 | 10 | 10 | 10 |
Epididymal spermatozoal measurements | ||||
Sperm motility (%) | 90.25 ± 0.34 | 88.31 ± 0.86 | 89.74 ± 0.80 | 87.95 ± 1.08 |
Sperm (103/mg cauda epididymis) | 704.8 ± 64.9 | 690.7 ± 55.9 | 537.5 ± 27.0* | 445.8 ± 13.5** |
Sperm (106/cauda epididymis) | 24.45 ± 0.95 | 18.40 ± 0.41** | 16.48 ± 0.72** | 14.64 ± 0.25** |
* Significantly different (P≤0.05) from the chamber control group by Shirley’s test
** P≤0.01
Applicant's summary and conclusion
- Conclusions:
- The NOAEC for females is 50 ppm based on minimal to moderate hyperplasia observed in the transitional epithelium of the urinary bladder in animals treated from 100 ppm.
The LOAEC for males is 100 ppm based on significantly decreased sperm count per mg cauda in males treated at 200 and 400 ppm and in cauda sperm counts in 100, 200, and 400 ppm groups.
However, the relevance of these effects can be questioned: first, the heat fixation at 65°C of caudae samples for sperm counts may have altered the integrity of the samples; secondly, these changes in sperm levels were not corroborated by other findings such as histopathological changes in other reproductive organs/tissues or other sperm parameters (motility, spermatid counts, etc.). Also, these decreases might be secondary to stress induced by hyperplasia of bladder epithelium at the 3 highest doses. However, in a conservative approach, this effect was selected as the critical effect to calculate DNELs.
The study suffers from several limitations:
- animals were exposed whole body by inhalation which likely resulted in systemic exposure much higher than intended exposure from target doses (animals likely exposed by oral route through grooming).
- the heat fixation at 65°C of caudae samples for sperm counts may have altered the integrity of the samples - Executive summary:
In a 90-day inhalation study conducted by NTP similarly to OECD guideline 413, groups of 10 animals per dose and per sex were administered for 6 hours per day, 5 days per week at 0, 25, 50, 100, 200 and 400 ppm for a total of 14 weeks. The animals were observed twice per day and weighed once per week. A complete histopathologic evaluation including treatment-related gross lesions was performed on all animals.
Treatment-related lesions (target organs) were identified and these organs and gross lesions were examined to a no-effect level.
Similar effects were observed in male and female mice from the same dose level (100 ppm): minimal to moderate hyperplasia observed in the transitional epithelium of the urinary bladder.
Decreased numbers of sperm per mg cauda in 200 and 400 ppm males and cauda sperm in 100, 200, and 400 ppm males were observed. However, the relevance of these effects can be questioned: first, the heat fixation at 65°C of caudae samples for sperm counts may have altered the integrity of the samples; secondly, these changes in sperm levels were not corroborated by other findings such as histopathological changes in other reproductive organs/tissues or other sperm parameters (motility, spermatid counts, etc.). Also, these decreases might be secondary to strss induced by hyperplasia of bladder epithelium at the 3 highest doses. In addition, animals were exposed whole body by inhalation, which likely resulted in systemic exposure much higher than intended exposure from target doses (animals likely exposed by oral route through grooming). However, in a conservative approach, this effect was selected as the critical effect to calculate DNELs.
The NOAEC for female mice is 50 ppm based on minimal to moderate hyperplasia observed in the transitional epithelium of the urinary bladder in animals treated at 100 to 400 ppm. The LOAEC for males is 100 ppm based on significantly decreased sperm count per mg cauda in males treated at 200 and 400 ppm and in cauda sperm counts in 100, 200, and 400 ppm groups.
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