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EC number: 202-795-1 | CAS number: 99-86-5
- 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
Developmental toxicity / teratogenicity
Administrative data
- Endpoint:
- developmental toxicity
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Remarks:
- Test method equivalent to OECD guideline 414
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 1 996
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- Deviations:
- yes
- Remarks:
- (2 treated groups with fewer than 16 pregnant dams)
- GLP compliance:
- not specified
- Limit test:
- no
Test material
- Reference substance name:
- p-mentha-1,3-diene
- EC Number:
- 202-795-1
- EC Name:
- p-mentha-1,3-diene
- Cas Number:
- 99-86-5
- Molecular formula:
- C10H16
- IUPAC Name:
- 1-isopropyl-4-methylcyclohexa-1,3-diene
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Wistar
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Oswaldo Cruz Central Animal House breeding stock.
- Age at study initiation: no data
- Weight at study initiation: 227 ± 22 to 240 ± 23 g
- Housing: animals were housed in standard plastic cages with stainless-steel cover lids and wood shavings as bedding.
- Diet (e.g. ad libitum): pelleted diet (Nuvital ®, Nuvilab Ltd, Curitiba, PR, Brazil), ad libitum.
- Water (e.g. ad libitum): Tap water, ad libitum.
- Acclimation period: no data
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 23 ± 1ºC
- Humidity (%): 70 %
- Photoperiod: dark/light cycle (lights on from 10.00 hr to 22.00 hr).
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- corn oil
- Remarks:
- (Mazola ®)
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
No info.
VEHICLE
- Concentration in vehicle: no info.
- Amount of vehicle (if gavage): 3.75 g/kg bw - Analytical verification of doses or concentrations:
- not specified
- Details on mating procedure:
- - Impregnation procedure: cohoused
- If cohoused: Mating was performed by transferring two females to the cage of one male for 2 hr (08.00-10.00 hr).
- M/F ratio per cage: 1 male/2 female
- Proof of pregnancy: Sperm in vaginal smear referred to as day 0 of pregnancy - Duration of treatment / exposure:
- From the 6th to 15th day of pregnancy
- Frequency of treatment:
- Daily
- Duration of test:
- 21 days (from day 0 to day 21 of pregnancy)
Doses / concentrationsopen allclose all
- Dose / conc.:
- 30 mg/kg bw/day
- Dose / conc.:
- 60 mg/kg bw/day
- Dose / conc.:
- 125 mg/kg bw/day
- Dose / conc.:
- 250 mg/kg bw/day
- No. of animals per sex per dose:
- Pregnant female rats per group: 24 (control), 14 (30 mg/kg bw/d), 18 (60 mg/kg bw/d), 25 (125 mg/kg bw/d) and 15 (250 mg(kg bw/d)
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale: Not specified.
Examinations
- Maternal examinations:
- BODY WEIGHT: Yes
- Time schedule for examinations: All rats were weighed on days 0, 6 up to 15 and 21 of pregnancy.
POST-MORTEM EXAMINATIONS: Yes
- Sacrifice on gestation day 21
- Organs examined: On day 21 of pregnancy the female rats were anaesthetized with ethyl ether inhalation and killed by decapitation. The gravid uterus was weighed with its contents. - Ovaries and uterine content:
- The uterine content was examined after termination: Yes
Examinations included:
- Gravid uterus weight: Yes.
- Number of corpora lutea: Yes.
- Number of implantations: Yes. The number of implantation sites was determined by the method of Salewski (1964).
- Number of resorptions: Yes.
- Other: Sex ratio, weight and viability of fetuses were determined. - Fetal examinations:
- - External examinations: Yes: [all per litter]
- Soft tissue examinations: Yes: [1/3 per litter]. By a microsectioning technique adapted from Sterz (1977). Heart, lungs, thymus, spleen, liver and kidneys of foetuses, which were microdissected, were also weighed.
- Skeletal examinations: Yes: [2/3 per litter]. According to the method of Dawson. - Statistics:
- Data were evaluated by one-way analysis of variance or, alternatively, by the Kruskal-Wallis test whenever the data did not fit a normal distribution. Differences between groups were tested by the two-sided Student's t-test or Mann-Whitney U-test. Proportions were analysed by the chi-square test or Fischer's exact test. Statistical evaluation was performed using a MINITAB program (MTB, University of Pennsylvania, 1984), and a difference was considered significant at P < 0.05.
Results and discussion
Results: maternal animals
General toxicity (maternal animals)
- Clinical signs:
- not specified
- Dermal irritation (if dermal study):
- not examined
- Mortality:
- not specified
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- There was no statistically significant difference in pregnancy weight gain between the control and the groups treated with 30 and 60 mg TER/kg body weight but marked reductions in weight gain during the treatment period (days 6-15) were observed in rats exposed to the two highest doses tested (125 and 250mg/kg body weight).
Furthermore, a statistically significant reduction in total pregnancy weight gain minus gravid uterus weight was found at these two highest doses tested (125 and 250mg/kg body weight). - 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
- Description (incidence and severity):
- Treatment did not influence drinking-water consumption.
- Ophthalmological findings:
- not examined
- Haematological findings:
- not examined
- 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:
- not specified
- Gross pathological findings:
- no effects observed
- Description (incidence and severity):
- At caesarian section no gross pathological alteration was found in the maternal organs of any group.
- Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- not examined
- Histopathological findings: neoplastic:
- not examined
- Other effects:
- no effects observed
Maternal developmental toxicity
- Number of abortions:
- not specified
- Pre- and post-implantation loss:
- no effects observed
- Description (incidence and severity):
- Neither the number of corpora lutea graviditatis/dam nor the number of visible implantation sites/litter were altered by TER over the dose range tested.
- Total litter losses by resorption:
- no effects observed
- Description (incidence and severity):
- In any of the TER-treated groups the number of resorptions/litter and the ratio of resorptions/implantation sites were not increased above that of the controls.
- Early or late resorptions:
- not specified
- Dead fetuses:
- no effects observed
- Description (incidence and severity):
- No alteration in the number of live foetuses/litter was noted in TER treated dams.
- Changes in pregnancy duration:
- not specified
- Changes in number of pregnant:
- effects observed, treatment-related
- Description (incidence and severity):
- The ratio of pregnant (i.e. rats with implantation sites detected by the method of Salewski at term)/sperm-positive treated dam did not differ significantly from that of the control group in rats treated with doses up to 125 mg TER/kg body weight but it was reduced at 250 mg TER/kg body weight.
- Other effects:
- no effects observed
Effect levels (maternal animals)
open allclose all
- Key result
- Dose descriptor:
- LOEL
- Effect level:
- 125 mg/kg bw/day
- Based on:
- test mat.
- Basis for effect level:
- body weight and weight gain
- Key result
- Dose descriptor:
- LOEL
- Effect level:
- 250 mg/kg bw/day
- Based on:
- test mat.
- Basis for effect level:
- changes in number of pregnant
Maternal abnormalities
- Key result
- Abnormalities:
- no effects observed
Results (fetuses)
- Fetal body weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- A significant reduction in foetal body weight was noted at the highest dose (250mg/kg body weight). No statistically significant reduction in foetal body weight was observed at doses lower than 250 mg/kg body weight.
- Reduction in number of live offspring:
- no effects observed
- Description (incidence and severity):
- There were no substance-related and/or statistically significant differences between the treated groups and the control group in the number of viable fetuses.
- Changes in sex ratio:
- no effects observed
- Description (incidence and severity):
- The sex distribution of the fetuses in the treated groups was comparable with the control fetuses. The differences observed in comparison to the control are without any biological relevance.
- Changes in litter size and weights:
- no effects observed
- Changes in postnatal survival:
- not examined
- External malformations:
- effects observed, non-treatment-related
- Description (incidence and severity):
- Except for a higher frequency of kinky tail in the group exposed to 30 mg TER/kg body weight and a higher proportion of foetuses with haematoma at the highest dose (250mg/kg body weight), no salient finding was revealed by external examination.
The increased frequency of tail abnormalities (bent tip and kinky tail) observed in foetuses exposed to TER was not related to dose and, in addition, the spontaneous frequency of kinky tail is relatively high in this rat strain (1%). - Skeletal malformations:
- effects observed, treatment-related
- Description (incidence and severity):
- Signs of delayed ossification (poorly ossified and not ossified bones as well as irregular spongy bones) were noted at doses higher than 30mg TER/kg body weight.
Also, a dose-related increase in the number of foetuses showing one or more abnormalities was found at doses higher than 30mg TER/kg body weight. These skeletal anomalies were manly higher incidences of os squamosum irregularly shaped, os supraoccipitale incompletely ossified, shorter ribs, extra ribs (cervical), sternum dislocated and os processus deltoid irregularly shaped. - Visceral malformations:
- no effects observed
- Description (incidence and severity):
- No increase in visceral malformations was observed in TER-treated groups.
- Other effects:
- effects observed, treatment-related
- Description (incidence and severity):
- The reduction in foetal weight noted at the highest dose was accompanied by a decrease in the absolute weights of heart, liver, lungs and thymus. The reduction in thymus weight was particularly pronounced and the relative weight [thymus weight (mg)/foetal weight (g)] of this organ was also decreased. In contrast with the effects of TER on the weight of other foetal organs, the kidneys were heavier in the groups treated with 125 and 250mg TER/kg body weight.
Effect levels (fetuses)
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 30 mg/kg bw/day
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- skeletal malformations
Fetal abnormalities
- Key result
- Abnormalities:
- effects observed, treatment-related
- Localisation:
- skeletal: skull
- skeletal: sternum
- skeletal: rib
- Description (incidence and severity):
- The overall increase in the occurrence of skeletal anomalies seems to result, to a large extent, from higher incidences of os squamosum irregularly shaped, os supraoccipitale incompletely ossified, shorter ribs, extra ribs (cervical), sternum dislocated and os processus deltoid irregularly shaped.
Overall developmental toxicity
- Key result
- Developmental effects observed:
- yes
- Lowest effective dose / conc.:
- 60 mg/kg bw/day
- Treatment related:
- yes
- Relation to maternal toxicity:
- developmental effects in the absence of maternal toxicity effects
- Dose response relationship:
- yes
- Relevant for humans:
- not specified
Any other information on results incl. tables
Table 1: Maternal weight gain of rats treated orally with alpha-terpinene on days 6-15 of pregnancy (a)
|
alpha-terpinene (mg/kg bw/day) |
||||
Treatment |
0 |
30 |
60 |
125 |
250 |
Treated females |
28 |
15 |
20b |
26 |
27 |
Pregnant females |
24 |
14 |
18 |
25 |
15 |
Pregnant/sperm positive females (%) |
86 |
93 |
90 |
96 |
56* |
Maternal weight (g) |
|||||
Day 0 |
227±20 |
230±22 |
229±11 |
227±18 |
240±23 |
Day 21 |
348±29 |
347±39 |
357±23 |
341±28 |
324±29* |
Gravid uterus weight (g) |
71.8±18.1 |
72.8±23.1 |
77.0±19.9 |
76.3±11.0 |
63.0±18.7 |
Maternal weight gain (g) |
|||||
Days 0-6 |
27.5±8.2 |
30.8±8.4 |
31.1±9.0 |
29.1±7.8 |
27.3±7.6 |
Days 6-11 |
13.6±5.7 |
16.9±5.7 |
11.8±5.8 |
6.3±7.1* |
-17.8±12.9* |
Days 6-15 |
30.7±21.9 |
35.7±9.4 |
29.2±6.8 |
21.0±9.1* |
1.4±9.7* |
Days 15-21 |
63.0±11.4 |
64.5±15.2 |
67.9±12.0 |
63.9±17.6 |
55.1±19.3 |
Days 0-21 |
121.2±21.9 |
131.1±23.2 |
128.3±17.4 |
114.1±22.1 |
83.7±27.1* |
Days 0-21 (minus uterus weight) |
49.4±15.6 |
58.3±11.5 |
51.2±14.4 |
37.7±19.0* |
20.7±13.7* |
a One pregnant female delivered on day 20.
b Percentage of pregnant females was analysed by the chi-square test. All other parameters were analysed by one-way analysis of variance and Student’s t-test. Values are mean ± SD.
*p < 0.05 v. controls.
Table 2: Parameters assessed at caesarean section of rats treated orally with alpha-terpinene on days 6-15 of pregnancy (a)
|
alpha-terpinene (mg/kg bw/day) |
||||
|
0 |
30 |
60 |
125 |
250 |
Corpa lutea |
12.5±3.0 |
12.9±2.1 |
12.6±2.5 |
12.9±1.8 |
12.1±2.9 |
Implantation sites |
|||||
Total |
306 |
179 |
232 |
327 |
189 |
Per litter |
12.6±3.2 |
12.8±3.8 |
12.9±3.1 |
13.2±1.9 |
12.6±2.4 |
Resorptions |
|||||
Total |
37 |
27 |
15 |
27 |
24 |
Resorptions/implantations (%) |
12.1 |
15.1 |
6.5 |
8.2 |
12.7 |
Live foetuses |
|||||
Total |
275 |
158 |
218 |
299 |
165 |
Foetuses/implantations (%) |
88 |
85 |
94 |
92 |
87 |
Per litter |
11.5±3.1 |
11.2±3.9 |
12.1±3.1 |
11.9±1.9 |
11.0±3.3 |
Foetal weight (g) |
|||||
Individual |
4.7±0.3 |
4.8±0.4* |
4.8±0.4* |
4.7±0.4 |
4.1±0.5* |
Litter |
4.7±0.2 |
4.9±0.3 |
4.8±0.3 |
4.7±0.4 |
4.0±0.4* |
Sex ratio (M/F) |
139/130 |
70/82 |
115/102 |
160/140 |
85/80 |
a Proportions were analysed by the chi-square test. All other parameters were analysed by one-way analysis of variance and Student’s t-test. Values are mean ± SD.
*p < 0.05 v. controls.
Table 3: Signs of delayed ossification in foetuses of rats treated with alpha-terpinene on days 6-15 of pregnancy (a)
|
alpha-terpinene (mg/kg bw/day) |
||||
|
0 |
30 |
60 |
125 |
250 |
Foetuses examined |
189 |
109 |
151 |
207 |
114 |
Foetuses with signs of delayed ossification (%) |
11.1 |
14.7 |
53.0* |
73.4* |
88.6* |
Foetuses (%) with retarded ossification in |
|||||
Skull bones |
0.5 |
4.6* |
2.6 |
2.9* |
16.6* |
Vertebral column |
1.6 |
0.9 |
22.5* |
34.8* |
21.0* |
Sternum |
11.6 |
5.5* |
45.0* |
70.0* |
87.7* |
Ribs |
0 |
0 |
6.0* |
13.5* |
6.1* |
Forelimbs |
1.6 |
1.8 |
13.2* |
9.2* |
9.6* |
Hindlimbs |
4.8 |
9.2 |
37.7* |
37.2* |
47.4* |
Signs of delayed ossification: not ossified (whole bone not stained); poorly ossified (whole bone is poorly ossified); and irregular spongy bones.
a Data were analysed by the chi-square test.
*p < 0.05 v. controls.
Table 4: Externally visible and visceral anomalies in foetuses of rats treated orally with alpha-terpinene on days 6-15 of pregnancy (a)
|
alpha-terpinene (mg/kg bw/day) |
||||
Treatment |
0 |
30 |
60 |
125 |
250 |
External examination (no. of foetuses) |
275 |
158 |
218 |
299 |
165 |
Foetuses with anomalies (%) |
|||||
Haematoma |
10 (3.6) |
7 (4.4) |
7 (3.2) |
16 (5.3) |
13 (7.9) |
Tail |
|||||
Bent end |
1 (0.4) |
0 |
2 (0.9) |
6 (2.0) |
4 (2.4) |
Kinky |
3 (1.1) |
10 (6.3)* |
3 (1.4) |
6 (2.0) |
5 (3.0) |
Pale |
0 |
0 |
1 (0.4) |
0 |
0 |
Oedema |
1 (0.4) |
0 |
0 |
0 |
0 |
Irregular positioning of forepaws |
0 |
1 (0.6) |
0 |
4 (1.3) |
0 |
Irregular positioning of hindpaws |
2 (0.7) |
2 (1.3) |
1 (0.4) |
3 (1.0) |
2 (1.2) |
Visceral examination (no. of foetuses) |
86 |
49 |
67 |
92 |
51 |
Foetuses with anomalies (%) |
|||||
Spleen (ectopic) |
1 (1.2) |
0 |
0 |
0 |
0 |
Heart (smaller) |
0 |
1 (2.0) |
0 |
0 |
0 |
Liver (smaller) |
1 (1.2) |
0 |
0 |
0 |
0 |
Adrenal gland (smaller) |
0 |
0 |
1 (1.5) |
0 |
0 |
Testes (ectopic) |
3 (3.5) |
0 |
1 (1.5) |
1 (1.1) |
0 |
Ureter (thicker) |
0 |
0 |
0 |
0 |
1 (2.0) |
a Proportions were analysed by the chi-square test or, alternatively, by Fischer’s exact test.
*p < 0.05 v. controls
Table 5: Foetal organ weight in rats treated orally with alpha-terpinene on days 6-15 of pregnancy (a)
|
alpha-terpinene (mg/kg bw/day) |
||||
Treatment |
0 |
30 |
60 |
125 |
250 |
Foetuses examined |
86 |
49 |
67 |
92 |
51 |
Foetal body weight (g) |
4.9±0.5 |
5.3±0.5 |
5.3±0.4 |
5.2±0.5 |
4.2±0.5* |
Foetal organ weights (mg) |
|||||
Spleen |
4.9±1.5 |
4.0±1.8 |
4.8±1.6 |
4.7±1.8 |
4.7±1.4 |
Heart |
29.1±5.0 |
29.9±5.0 |
28.7±4.0 |
29.2±5.0 |
26.5±5.0* |
Liver |
370.0±66.0 |
372.0±48.0 |
375.0±39.0 |
362±80.0 |
335.0±64.0 |
Kidneys |
|||||
Right |
10.8±2.0 |
11.1±1.7 |
12.2±1.7* |
12.1±2.4* |
11.8±2.0* |
Left |
10.4±2.2 |
10.4±1.6 |
11.4±1.7* |
11.1±2.0* |
12.0±2.0* |
Lung |
143.0±18.0 |
139.0±12.0 |
142.0±14.0 |
138.0±15.0* |
131.0±24.0* |
Thymus |
7.6±1.1 |
7.4±1.5 |
8.0±1.4 |
7.5±1.6 |
5.3±1.7* |
a Data were analysed by one-way analysis of variance and Student’s t-test. Values are mean ± SD.
*p < 0.05 v. controls.
Table 6: Skeletal anomalies in foetuses of rats treated orally with alpha-terpinene on days 6-15 of pregnancy (a)
|
alpha-terpinene (mg/kg bw/day) |
||||
|
0 |
30 |
60 |
125 |
250 |
Foetuses examined |
189 |
109 |
151 |
207 |
114 |
Foetuses with skeletal anomalies (%) |
19.6 |
27.5 |
33.1 |
61.3 |
89.5 |
Foetuses (%) showing anomalies in: |
|||||
Skull |
5.3 |
8.2 |
16.5* |
34.8* |
63.1* |
Os basisphenoid Bifurcated |
0 |
0.9 |
0.7 |
0 |
0 |
Os basoccipitale Irregular shape |
0 |
0 |
0 |
0 |
1.7 |
Os squamosum Irregular shape |
4.8 |
6.4 |
13.2* |
24.6* |
35.1* |
Os frontale Distance too large |
0 |
0.9 |
0 |
0 |
0.9 |
Os interparietale Bone hole |
0 |
0 |
0 |
0 |
0.9 |
Os palatinum Bone hole |
0 |
0 |
1.3 |
1.4 |
0.9 |
Os parietale Distance too large |
0 |
0.9 |
0 |
1.0 |
0.9 |
Os suproccipitale |
|||||
Discontinuous |
0 |
0 |
0 |
0 |
0.9 |
Gap |
0 |
0 |
0 |
0.5 |
0.9 |
Incomplete ossification |
0.5 |
0.9 |
2.6 |
12.6* |
36.0* |
Os tympanicum Discontinuous |
0 |
0 |
0 |
0 |
0.9 |
Vertebral column |
0 |
0.9 |
0 |
0 |
2.6 |
Atlas |
|||||
Thicker |
0 |
0 |
0 |
0 |
1.7 |
Cervical vertebra |
|||||
Irregular shape |
0 |
0 |
0 |
0 |
0.9 |
Fused |
0 |
0 |
0 |
0 |
0.9 |
Thoracic vertebra |
|||||
Fused with rib |
0 |
0 |
0 |
0 |
0.9 |
Two ossification centra |
0 |
0.9 |
0 |
0 |
0.9 |
Ribs |
6.9 |
10.1 |
8.6 |
20.3* |
53.5* |
Shorter |
5.8 |
6.4 |
6.0 |
19.8* |
50.0* |
Extra |
|||||
Cervical |
0.5 |
0.9 |
1.3 |
1.0 |
7.0* |
Lumbar |
0.5 |
2.7 |
1.3 |
1.0 |
0.9 |
Sternum |
5.8 |
5.5 |
3.3 |
8.2 |
11.4* |
Dislocated |
5.8 |
5.5 |
3.3 |
8.2 |
11.4* |
Forelimbs |
2.6 |
5.5 |
6.6 |
17.9* |
6.1 |
Irregular position |
0.5 |
0.9 |
0 |
2.9 |
0 |
Os processus deltoid |
|||||
Bone hole |
1.6 |
0 |
1.3 |
1.9 |
3.5 |
Irregular shape |
0.5 |
4.6 |
6.6 |
14.5 |
2.6 |
a Data were analysed by the chi-square test.
*p < 0.05 v. controls.
Applicant's summary and conclusion
- Conclusions:
- Under the test conditions, alpha terpinene can adversely affect embryofoetal development in the rat at oral doses higher than 60 mg/kg body weight and is toxic to the mother at oral doses higher than 125 mg/kg body weight. Thus, the NOAEL of alpha terpinene for embryofoetal toxicity was determined to be 30 mg/kg body weight.
- Executive summary:
A pre-natal developmental toxicity test was performed with alpha terpinene following a method equivalent to OECD Guideline 414. Alpha terpinene dissolved in corn oil at doses of 30, 60, 125 and 250 mg/kg body weight was given by gavage to female Wistar rats from day 6 to 15 of pregnancy. Caesarean sections were performed on day 21 of pregnancy. The number of implantation sites, living and dead foetuses, resorptions and corpora lutea were recorded. All foetuses were weighed and examined for externally visible malformations. One-third of the foetuses of each litter were evaluated for visceral anomalies. The remaining foetuses were examined for skeletal malformations. A reduction in body weight minus uterine weight at term indicated that the two highest doses tested (125 and 250mg/kg bw) were maternally toxic. No increase in the ratio of resorptions/implantations was observed over the dose range tested. The highest dose (250 mg/kg bw) reduced the ratio of pregnant/treated female. A decrease in foetal body weight and an increase in foetal kidney weights were noted at 250 mg /kg bw. Signs of delayed ossification (poorly ossified and not ossified bones as well as irregular spongy bones) and a higher incidence of minor skeletal malformations were observed at doses of 60 mg/kg bw or more. These findings indicate that the NOAEL for alpha terpinene-induced embryofoetotoxicity can be set at 30 mg/kg bw by the oral route.
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