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EC number: 227-815-6 | CAS number: 5989-54-8
- 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
- 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
Endpoint summary
Administrative data
Key value for chemical safety assessment
Effects on fertility
Description of key information
No study on toxicity to reproduction was available for l-limonene. No effects were observed on sexual organs in the NTP 90-d study conducted in rats and mice exposed to d-limonene (gross pathology and histopathology examination of prostate/testes or ovaries/uterus).
Link to relevant study records
- Endpoint:
- screening for reproductive / developmental toxicity
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- the study does not need to be conducted because a pre-natal developmental toxicity study is available
- other:
- Reason / purpose for cross-reference:
- data waiving: supporting information
- Reason / purpose for cross-reference:
- data waiving: supporting information
- Reason / purpose for cross-reference:
- data waiving: supporting information
- Reason / purpose for cross-reference:
- data waiving: supporting information
- Reason / purpose for cross-reference:
- data waiving: supporting information
- Reproductive effects observed:
- not specified
Reference
Effect on fertility: via oral route
- Endpoint conclusion:
- no study available
Effect on fertility: via inhalation route
- Endpoint conclusion:
- no study available
Effect on fertility: via dermal route
- Endpoint conclusion:
- no study available
Additional information
No study on toxicity to reproduction was available for l-limonene. In developmental toxicity studies, with detailed results but limited information on test conditions, d-limonene did not ellicit any teratogenic effects in tested rabbits, mice or rats. Based on the absence of observed teratogenic effects and on the absence of effects on sexual organs in the NTP 90-d study conducted in rats and mice (gross pathology and histopathology examination of prostate/testes or ovaries/uterus), a toxicity to reproduction study is deemed not to be scientifically justified. Moreover, European Food Safety Authority made a review of the toxicologic properties of d-limonene in 2010, and concluded on the absence of safety concern due to to d-limonene intake, with no specific concern related to the absence of any study for toxicity to reproduction for this substance (EFSA Journal 2010; 8(5): 1334).
For further information on read-across justification, see section 13: point "read-across approach"
Effects on developmental toxicity
Description of key information
Weight of evidence: d-limonene was not teratogenic in rabbit fetuses and the NOAEL for fetal toxicity was considered to be greater than the highest dose tested. In two developmental toxicity studies in rats and mice, slight ossification delays/malformations and organ weights changes were observed but not dose-related and/or observed at doses where maternal toxicity was identified.
Link to relevant study records
- Endpoint:
- developmental toxicity
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- weight of evidence
- Study period:
- 1977
- Reliability:
- 4 (not assignable)
- Rationale for reliability incl. deficiencies:
- other: Read-across from an analogue substance for which there is available information (Klimish=4)
- Justification for type of information:
- REPORTING FORMAT FOR THE ANALOGUE APPROACH
See cross-reference to justification of read-across. - Reason / purpose for cross-reference:
- read-across source
- Reason / purpose for cross-reference:
- read-across: supporting information
- Details on maternal toxic effects:
- Maternal toxic effects:yes
Details on maternal toxic effects:
Treatment with the highest dose level (1000 mg/kg) of d-limonene resulted in death of dams with less than 40% mortality. The significant decrease of body- weight gain and food consumption were temporarily observed in dams given 500 and 1000 mg/kg of d-limonene, but no anomalies were observed in the general behaviour of dams given 250 and 500 mg/kg of d-limonene during the gestation. - Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 250 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Basis for effect level:
- body weight and weight gain
- mortality
- Remarks on result:
- other: Based on the read-across from an analogue substance.
- Key result
- Abnormalities:
- no effects observed
- Details on embryotoxic / teratogenic effects:
- Embryotoxic / teratogenic effects:no effects
Details on embryotoxic / teratogenic effects:
- External examination of fetuses showed no anormalies.
- Visceral and skeletal examinations revealed some anormalies such as incomplete lobulation of the lungs, enlargement of the foramen ovale and retarded ossification of the middle phalanx of fore limbs in addition to the 5th sternebrae. These did not appear to be dose-dependent and restored to normal during the postnatal development.
- Other non specific anormalies involved the lumber ribs in fetuses and offsprings, formation of the accessory ossification center of the 5th sternebrae in offsprings and the atrial septal defect detected in only 2 fetuses of a litter from dams treated with 250 mg/kg bw/day of d-limonene. - Dose descriptor:
- NOAEL
- Effect level:
- > 1 000 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Basis for effect level:
- other: fetotoxicity
- Abnormalities:
- not specified
- Developmental effects observed:
- not specified
- Conclusions:
- Based on the read-across from the analogue substance d-limonene, l-limonene is not considered to have teratogenic potential in rabbit, the NOAEL for fetal toxicity was estimated to be greater than 1000 mg/kg bw/day. The NOAEL for maternal toxicity was estimated to be 250 mg/kg bw/day based on the decreased bodyweight gain.
- Executive summary:
Based on the read-across from the analogue substance d-limonene, l-limonene is not considered to have teratogenic potential in rabbit, the NOAEL for fetal toxicity is estimated to be greater than 1000 mg/kg bw/day. The NOAEL for maternal toxicity is estimated to be 250 mg/kg bw/day based on the decreased bodyweight gain.
- Endpoint:
- developmental toxicity
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- weight of evidence
- Study period:
- 1977
- Reliability:
- 4 (not assignable)
- Rationale for reliability incl. deficiencies:
- other: Read-across from an analogue substance for which there is available information (Klimish=4)
- Justification for type of information:
- REPORTING FORMAT FOR THE ANALOGUE APPROACH
See cross-reference to justification of read-across. - Reason / purpose for cross-reference:
- read-across source
- Reason / purpose for cross-reference:
- read-across: supporting information
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 591 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Basis for effect level:
- body weight and weight gain
- Remarks on result:
- other: Based on the read-across from an analogue substance.
- Key result
- Abnormalities:
- no effects observed
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 591 mg/kg bw/day
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: Increased incidences of abnormal skeletal formation in fetuses and decreased bodyweight gain in male offsprings born to dams administered with 2363 mg/kg-bw/day
- Remarks on result:
- other: Based on the read-across from the analogue substance d-limonene.
- Key result
- Abnormalities:
- effects observed, treatment-related
- Localisation:
- skeletal: rib
- Description (incidence and severity):
- Lumber rib and fused rib in the fetuses
- Key result
- Developmental effects observed:
- yes
- Lowest effective dose / conc.:
- 2 363 mg/kg bw/day
- Treatment related:
- yes
- Relation to maternal toxicity:
- not specified
- Dose response relationship:
- no
- Relevant for humans:
- not specified
- Conclusions:
- Based on the read-across from the analogue substance d-limonene, the NOAEL for maternal and fetal toxicity of l-limonene was estimated to be 591 mg/kg bw/day based on the decreased bodyweight gain in dams and increased incidences of abnormal bone formation in fetuses.
- Executive summary:
Based on the read-across from the analogue substance d-limonene, the NOAEL for maternal and fetal toxicity of l-limonene was estimated to be 591 mg/kg bw/day based on the decreased bodyweight gain in dams and increased incidences of abnormal bone formation in fetuses.
- Endpoint:
- developmental toxicity
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- weight of evidence
- Reliability:
- 4 (not assignable)
- Rationale for reliability incl. deficiencies:
- other: Read-across from an analogue substance for which there is available information (Klimish=4)
- Justification for type of information:
- REPORTING FORMAT FOR THE ANALOGUE APPROACH
See cross-reference to justification of read-across. - Reason / purpose for cross-reference:
- read-across source
- Reason / purpose for cross-reference:
- read-across: supporting information
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 591 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Basis for effect level:
- body weight and weight gain
- mortality
- Remarks on result:
- other: Based on the read-across from an analogue substance.
- Key result
- Abnormalities:
- no effects observed
- Details on embryotoxic / teratogenic effects:
- Embryotoxic / teratogenic effects:yes
Details on embryotoxic / teratogenic effects:
Prolongation of the ossification of metacarpals and proximal phalanges in fetuses, decreased bodyweight gain (male offsprings) and organ weights at 2869 mg/kg bw/day - Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 591 mg/kg bw/day
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: prolongation of the ossification of metacarpals and proximal phalanges in fetuses, decreased bodyweight gain (male offsprings) and organ weights at 2869 mg/kg bw/day
- Remarks on result:
- other: Based on the read.across from an analogue substance.
- Key result
- Abnormalities:
- effects observed, treatment-related
- Localisation:
- other: prolongation of the ossification of metacarpals and proximal phalanges in fetuses, decreased bodyweight gain (male offsprings) and organ weights at 2869 mg/kg bw/day
- Key result
- Developmental effects observed:
- yes
- Lowest effective dose / conc.:
- 2 869 mg/kg bw/day
- Treatment related:
- yes
- Relation to maternal toxicity:
- not specified
- Dose response relationship:
- no
- Relevant for humans:
- not specified
- Conclusions:
- Based on the read-across from the analogue substance d-limonene, the NOAEL for maternal toxicity of l-limonene was estimated to be 591 mg/kg bw/day based on the deaths and decreased bodyweight gain and the NOAEL for fetal toxicity was estimated to be 591 mg/kg bw/day based on the delayed skeletal formation and decreased bodyweight gain.
- Executive summary:
Based on the read-across from the analogue substance d-limonene, the NOAEL for maternal toxicity of l-limonene was estimated to be 591 mg/kg bw/day based on the deaths and decreased bodyweight gain and the NOAEL for fetal toxicity was estimated to be 591 mg/kg bw/day based on the delayed skeletal formation and decreased bodyweight gain.
Referenceopen allclose all
Table 1: Effect of d-limonene on prenatal development of rabbit fetuses
Dose (mg/kg bw) |
Control |
250 |
500 |
1000 |
No. of pregnant animals |
10 |
10 |
10 |
18 |
No. of dead clams |
0 |
0 |
0 |
6 |
(%) |
|
|
|
33 |
No. of examined clams |
10 |
10 |
10 |
10 |
No. of implantations |
96 |
94 |
85 |
91 |
(mean ± S.E.) |
9.50 ± 0.25 |
9.40 ± 0.21 |
8.50 ± 0.33 |
9.10 ± 0.25 |
No. of resorbed fetuses |
5 |
4 |
4 |
8 |
No. of dead fetuses |
3 |
5 |
0 |
3 |
No. of live fetuses |
88 |
85 |
81 |
80 |
Sex ratio (Male/Female) |
0.73 (37/51) |
1.13 (45/50) |
0.62 (31/50) |
1.11 (38/42) |
Fetus body weight (g) |
|
|
|
|
Male (mean ± S.E.) |
44.39 ± 1.33 |
48.09 ± 1.07 * |
44.76 ± 1.51 |
43.22 ± 0.96 |
Female (mean ± S.E.) |
45.64 ± 1.00 |
47.45 ± 1.08 |
46.14 ± 1.21 |
45.13 ± 1.10 |
Placental weight (g) |
|
|
|
|
Male (mean ± S.E.) |
5.76 ± 0.17 |
5.84 ± 0.17 |
5.95 ± 0.29 |
5.77 ± 0.19 |
Female (mean ± S.E.) |
5.87 ± 0.19 |
5.70 ± 0.15 |
6.16 ± 0.18 |
5.87 ± 0.23 |
* Significantly different from the control at 5% level
Table 2: Prenatal examinations of rabbit fetuses
Dose (mg/kg bw) |
Control |
250 |
500 |
1000 |
External examination |
|
|
|
|
No. of examined fetuses |
91 |
90 |
81 |
83 |
No. of malforrned fetuses |
0 |
0 |
0 |
0 |
Visceral examination |
|
|
|
|
No. of examined fetuses |
88 |
85 |
81 |
80 |
No. of malformed fetuses |
|
|
|
|
Atrial septal defect (%) |
0 |
2 (2.4) |
0 |
0 |
No. of minor abnormality |
|
|
|
|
Incomplete lobulation of lungs (%) |
11 (12.5) |
16 (18.8) |
19 (23.5) |
19 (23.8) |
Enlargement of foramen ovale (%) |
2 (2.3) |
2 (2.4) |
5 (6.2) |
4 (5.0) |
Skeletal examination |
|
|
|
|
No. of examined fetuses |
86 |
87 |
81 |
80 |
No. of malformed fetuses |
0 |
0 |
0 |
0 |
No. of variation |
|
|
|
|
Left lumbar rib (%) |
18 (20.9) |
26 (29.9) |
14 (17.3) |
25 (31.3) |
Right lumbar rib (%) |
16 (18.6) |
22 (25.3) |
14 (17.3) |
22( 27.5) |
Ossification pattern |
|
|
|
|
Retarded ossification of 5th sternebrae (%) |
11 (12.8) |
14 (16.1) |
8 (9.9) |
18 (22.5) |
Retarded ossification of middle phalanx of fore limbs (%) |
2 (2.3) |
3 (3.4) |
0 |
6 (7.4) |
Table 3: Absolute organ weights of rabbit offsprings
|
Male |
Female |
||||||
|
Control |
250 |
500 |
1000 |
Control |
250 |
500 |
1000 |
No. of offsprings |
13 |
12 |
8 |
13 |
10 |
13 |
16 |
9 |
Final body weight (g) |
893.0 ± 45.3 |
1021.2 ± 45.4 ** |
931.9 ± 55.5 |
957.3 ± 52.4 |
1005.5 ± 53.7 |
1093.1 ± 46.6 |
860.0 ± 31.6 * |
1071.7 ± 58.1 |
Liver (g) |
36.49 ± 2.52 |
45.08 ± 1.52 * |
38.67 ± 3.10 |
34.91 ± 2.76 |
41.79 ± 3.39 |
13.95 ± 3.18 |
34.68 ± 1.90 |
48.30 ± 6.14 |
Lungs (g) |
5.53 ± 0.35 |
6.25 ± 0.26 |
5.98 ± 0.36 |
5.46 ± 0.18 |
5.91 ± 0.25 |
5.94 ± 0.28 |
5.72 ± 0.18 |
5.93 ± 0.45 |
Heart (g) |
2.63 ± 0.17 |
3.50 ± 0.16 ** |
2.86 ± 0.17 |
3.04 ± 0.19 |
3.19 ± 0.17 |
3.38 ± 0.21 |
2.72 ± 0.12 * |
3.34 ± 0.20 |
Spleen (g) |
0.71 ± 0.05 |
0.77 ± 0.04 |
0.71 ± 0.08 |
0.81 ± 0.04 |
0.64 ± 0.06 |
0.74 ± 0.05 |
0.74 ± 0.04 |
0.78 ± 0.07 |
Thymus (g) |
2.31 ± 0.20 |
2.51 ± 0.23 |
2.11 ± 0.38 |
1.96 ± 0.11 |
2.40 ± 0.30 |
2.77 ± 0.19 |
1.671.14 * |
2.36 ± 0.31 |
Kidneys (g) |
7.67 ± 0.42 |
9.80 ± 0.46 ** |
8.29 ± 0.29 |
8.58 ± 0.52 |
8.82 ± 0.46 |
8.40 ± 0.30 |
7.86 ± 0.37 |
9.56 ± 0.55 |
Thyroids (mg) |
75.89 ± 8.35 |
102.68 ± 4.18* |
86.74 ± 10.97 |
80.93 ± 7.41 |
82.78 ± 8.00 |
89.90 ± 4.11 |
75.75 ± 5.43 |
96.30 ± 9.67 |
Adrenals (mg) |
69.65 ± 6.02 |
9.1.93 ± 1.06 ** |
78.79 ± 5.89 |
71.36 ± 6.00 |
82.23 ± 4.37 |
94.24 ± 5.07 |
87.64 ± 4.18 |
105.39 ± 15.11 |
Testes or Ovaries (mg) |
180.42 ± 17.15 |
272.86 ± 16.46 ** |
185.62 ± 23.78 |
162.84 ± 20.59 |
46.31 ± 7.90 |
46.10 ± 2.80 |
43.53 ± 2.69 |
47.77 ± 3.59 |
* Significantly different from the control at 5% level
** Significantly different from the control at 1% level
Table 4: Relative organ weights per 100 g of rabbit offsprings
|
Male |
Female |
||||||
|
Control |
250 |
500 |
1000 |
Control |
250 |
500 |
1000 |
No. of offsprings |
13 |
12 |
8 |
13 |
10 |
13 |
16 |
9 |
Final body weight (g) |
893.0 ± 45.3 |
1021.2 ± 45.4 ** |
931.9 ± 55.5 |
957.3 ± 52.4 |
1005.5 ± 53.7 |
1093.1 ± 46.6 |
860.0 ± 31.6 * |
1071.7 ± 58.1 |
Liver (g/100 g) |
4.08 ± 0.25 |
3.99 ± 0.22 * |
4.16 ± 0.26 |
3.52 ± 0.10 |
4.25 ± 0.17 |
4.03 ± 0.21 |
4.02 ± 0.16 |
4.04 ± 0.32 |
Lungs (g/100 g) |
0.61 ± 0.03 |
0.55 ± 0.03 |
0.65 ± 0.04 |
0.58 ± 0.03 |
0.62 ± 0.02 |
0.55 ± 0.02 * |
0.67 ± 0.03 |
0.51 ± 0.02 ** |
Heart (g/100 g) |
0.29 ± 0.01 |
0.31 ± 0.01 |
0.31 ± 0.01 |
0.31 ± 0.02 |
0.33 ± 0.01 |
0.31 ± 0.01 |
0.32 ± 0.01 |
0.29 ± 0.01 * |
Spleen (g/100 g) |
0.08 ± 0.01 |
0.07 ± 0.01 |
0.08 ± 0.01 |
0.08 ± 0 |
0.07 ± 0.01 |
0.07 ± 0.01 |
0.09 ± 0 |
0.07 ± 0.01 |
Thymus (g/100 g) |
0.25 ± 0.02 |
0.22 ± 0.02 |
0.25 ± 0.03 |
0.20 ± 0.01 * |
0.24 ± 0.03 |
0.25 ± 0.01 |
0.195 ± 0.01 |
0.20 ± 0.02 |
Kidneys (g/100 g) |
0.85 ± 0.04 |
0.86 ± 0.04 |
0.90 ± 0.03 |
0.88 ± 0.02 |
0.91 ± 0.02 |
0.80 ± 0.01 |
0.91 ± 0.01 |
0.83 ± 0.03 * |
Thyroids (mg/100 g) |
8.21 ± 0.69 |
9.10 ± 0.51 |
9.21 ± 0.87 |
8.18 ± 0.42 |
8.40 ± 0.56 |
8.41 ± 0.45 |
8.81 ± 0.57 |
8.13 ± 0.41 |
Adrenals (mg/100 g) |
7.82 ± 0.60 |
8.37 ± 0.40 |
8.58 ± 0.77 |
7.18 ± 0.28 |
8.61 ± 0.51 |
8.79 ± 0.57 |
9.15 ± 0.42 |
9.04 ± 0.14 |
Testes or Ovaries (mg/100 g) |
23.68 ± 1.31 |
19.68 ± 0.94 * |
19.48 ± 1.69 |
16.35 ± 1.56 |
5.15 ± 1.19 |
4.33 ± 0.32 |
5.19 ± 0.43 |
3.84 ± 0.32 |
* Significantly different from the control at 5% level
** Significantly different from the control at 1% level
Table 5: Effects of d-limonene on gross differentiations of rabbit offsprings
|
Control |
250 |
500 |
1000 |
No. of examined offsprings |
23 |
25 |
24 |
22 |
Days of gross differentiation after birth Opening of the ear-shell |
|
|
|
|
6th day (%) |
0 |
0 |
1 (4.2) |
0 |
7th day (%) |
23 (100) |
25 (100) |
23 (95.8) |
22 (100) |
Coating with the hair |
|
|||
2nd day (%) |
7 (30.4) |
0 |
0 |
0 |
3rd day (%) |
16 (69.6) |
25 (100) |
24 (100) |
22 (100) |
Odontiasis |
|
|||
At birth (%) |
23 (100) |
25 (100) |
24 (100) |
22 (100) |
Opening of the eyelids |
|
|||
9th day (%) |
0 |
0 |
0 |
3 (13.6) |
10th day (%) |
11 (47.8) |
4 (16.0) |
13 (54.2) |
5 (22.7) |
11th day (%) |
4 (17.4) |
15 (60.0) |
10 (41.7) |
12 (54.5) |
12th day (%) |
3 (13.0) |
5 (20.0) |
1 (4.2) |
2 (9.1) |
13th day (%) |
5 (21.7) |
1 (4.0) |
0 |
0 |
Table 6: Effects of d-limonene on postnatal development of rabbit offsprings
|
Control |
250 |
500 |
1000 |
No of dams |
3 |
3 |
3 |
3 |
No. of still-birth (Male/Female) |
1 (1/0) |
0 |
0 |
1 (0/1) |
No. of offsprings (Male/Female) At birth |
28 (15/13) |
27 (14/13) |
26 (8/18) |
27 (15/12) |
1st week |
28 (15/13) |
27 (14/13) |
25 (8/17) |
26 (14/12) |
2nd week |
26 (14/12) |
27 (14/13) |
25 (8/17) |
26 (14/12) |
3rd week |
24 (14/10) |
27 (14/13) |
25 (8/17) |
25 (14/11) |
4th week |
23 (13/10) |
26 (13/13) |
25 (8/17) |
22 (13/ 9) |
5th week |
23 (13/10) |
25 (12/13) |
25 (8/17) |
22 (13/ 9) |
6th week |
23 (13/10) |
25 (12/13) |
25 (8/17) |
22 (13/ 9) |
7th week |
23 (13/10) |
25 (12/13) |
24 (8/16) |
22 (13/ 9) |
Weanling rate (%) |
79.3 (81.2/76.9) |
92.6 (85.7/100) |
92.3 (100/88.9) |
78.6 (86.7/69.2) |
Table 7: Postnatal examinations of rabbit offsprings
|
Control |
250 |
500 |
1000 |
No. of dams |
3 |
3 |
3 |
3 |
No. of examined offsprings |
23 |
25 |
24 |
22 |
Sensory function |
Normal |
Normal |
Normal |
Normal |
External examination No. of malformed offsprings |
0 |
0 |
0 |
0 |
Visceral examination No. of malformed offsprings |
0 |
0 |
0 |
0 |
No. of minor abnormality Incomplete lobulation of lungs (%) |
2 (8.7) |
1 (4.0) |
0 |
0 |
Accessory spleen (%) |
2 (8.7) |
0 |
0 |
0 |
Protrusion of gall bladder (%) |
1 (4.3) |
1 (4.0) |
0 |
0 |
Skeletal examination No. of malformed offsprings |
0 |
0 |
0 |
0 |
No. of variation Left lumbar rib (%) |
4 (17.4) |
4 (16.0) |
4 (16.7) |
4 (18.2) |
Right lumbar rib (%) |
2 (8.7) |
6 (24.0) |
6 (25.0) |
4 (18.2) |
Translocation of caudal vertebrae (%) |
1 (4.3) |
0 |
1 (4.2) |
0 |
Ossification pattern Retarded ossification of 5th sternebrae (%) |
0 |
2 (8.0) |
0 |
1 (4.5) |
Accessory ossification center of 5th sternebrae (%) |
1 (4.3) |
2 (8.0) |
0 |
3 (13.6) |
Effect on developmental toxicity: via oral route
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- NOAEL
- 591 mg/kg bw/day
- Study duration:
- subacute
- Species:
- rat
- Quality of whole database:
- Read-across from the analogue substande d-limonene for which there are available information which have detailed results but limited information on test conditions (Klimish =4).
Effect on developmental toxicity: via inhalation route
- Endpoint conclusion:
- no study available
Effect on developmental toxicity: via dermal route
- Endpoint conclusion:
- no study available
Additional information
Develomental toxicity studies, with detailed results but limited information on test conditions (studies in Japanese), did not ellicit any teratogenic effects of d-limonene on tested rabbits, mice or rats.
In a prenatal developmental toxicity study, d-limonene was administered orally to groups of pregnant Japanese white rabbits at dose levels of 250, 500 and 1000 mg/kg bw/day for 13 days from Day 6 to 18 of gestation. External examination of fetuses showed no anormalies. Visceral and skeletal examinations revealed some anormalies such as incomplete lobulation of the lungs, enlargement of the foramen ovale and retarded ossification of the middle phalanx of fore limbs in addition to the 5th sternebrae but these effects were not dose-dependent. d-limonene was not teratogenic in rabbit fetuses and the NOAEL for fetal toxicity was considered to be greater than 1000 mg/kg bw/day.
In a prenatal developmental toxicity study, d-limonene was administered orally to groups of pregnant ICR mice (20/dose: 15 for teratogenicity study, 5 for postnatal development) at dose levels of 0, 591 and 2363 mg/kg bw/day for 6 days from Day 7 to 12 of gestation. A significant decrease of bodyweight gain in pregnant mice was observed at 2363 mg/kg bw/day. An incidence of lumber rib and fused rib in the fetuses increased significantly at 2363 mg/kg bw/day compared with those of control. In the observation of skeletal development in fetuses, retarded ossification of proximal phalanx of fore limb, metatarsal bone and proximal phalanx of hind limb were observed but were not dose-dependent or only observed at the highest dose, associated with maternal toxicity.
In a developmental toxicity study, d-limonene was administered orally to groups of pregnant Wistar rats (20/dose: 15 for teratogenicity study, 5 for postnatal development) at dose levels of 0, 591 and 2869 mg/kg bw/day for 7 days from Day 9 to 15 of gestation. At 2869 mg/kg bw/day, maternal bodyweight decreased and several mothers (40%) died during treatment. Delayed ossification of fetuses metacarpal bone and proximal phalanx at 2869 mg/kg bw/day was increased and a decreased tendency of bodyweight was noted in postnatal male offsprings born to mothers treated at 2869 mg/kg bw/day, compared with the control group. Thymus, spleen and ovaries weights decreased in offsprings born to mothers treated at 2869 mg/kg.
For further information on read-across justification, see section 13: point "read-across approach"
Justification for classification or non-classification
Harmonized classification:
No harmonized classification is available according to the Regulation (EC) No 1272/2008 .
Self classification:
All potential effects of d-limonene observed on reproduction and development were either associated with maternal toxicity, or not dose-related. In conclusion, based on the read-across approach, l-limonene should not be classified for toxicity to reproduction or develomental toxicity.
Additional information
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