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EC number: 284-521-0 | CAS number: 84929-38-4 Extractives and their physically modified derivatives such as tinctures, concretes, absolutes, essential oils, oleoresins, terpenes, terpene-free fractions, distillates, residues, etc., obtained from Citrus nobilis, Rutaceae.
- 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:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- weight of evidence
- Study period:
- 1975
- Reliability:
- 4 (not assignable)
- Rationale for reliability incl. deficiencies:
- other: Original reference in Japanese language
Cross-referenceopen allclose all
- Reason / purpose for cross-reference:
- reference to same study
- Reason / purpose for cross-reference:
- reference to other study
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 1 975
Materials and methods
- Principles of method if other than guideline:
- Prenatal developmental toxicity study: Groups of pregnant Wistar rats (20/dose: 15 for teratogenicity study, 5 for postnatal development) were administered orally with d-limonene at dose levels of 0, 591 and 2869 mg/kg bw/day suspended with 1% gum-arabic solution for 7 days from Day 9 to 15 of gestation and evaluated for developmental toxicity.
- GLP compliance:
- not specified
- Limit test:
- no
Test material
- Reference substance name:
- (R)-p-mentha-1,8-diene
- EC Number:
- 227-813-5
- EC Name:
- (R)-p-mentha-1,8-diene
- Cas Number:
- 5989-27-5
- Molecular formula:
- C10H16
- IUPAC Name:
- (4R)-1-methyl-4-(prop-1-en-2-yl)cyclohexene
- Reference substance name:
- Dipentene
- EC Number:
- 205-341-0
- EC Name:
- Dipentene
- Cas Number:
- 138-86-3
- IUPAC Name:
- 4-isopropenyl-1-methylcyclohexene
- Details on test material:
- - Name of test material (as cited in study report): d-limonene; d-p-mentha-1,8-diene
- Boiling point: 176-177 °C
- Specific gravity (at 25 °C): 0.8340-0.8420
Constituent 1
Constituent 2
Test animals
- Species:
- rat
- Strain:
- Wistar
- Details on test animals or test system and environmental conditions:
- No data
Administration / exposure
- Route of administration:
- oral: unspecified
- Vehicle:
- other: 1% gum-arabic solution
- Details on exposure:
- Volume administered: 5 mL/kg bw for all doses
- Analytical verification of doses or concentrations:
- not specified
- Details on analytical verification of doses or concentrations:
- None
- Details on mating procedure:
- no data
- Duration of treatment / exposure:
- 7 days (gestation Day 9-15)
- Frequency of treatment:
- Once daily
- Duration of test:
- Gestation Day 0 to postnatal week 7
Doses / concentrations
- Remarks:
- Doses / Concentrations:
0, 591 and 2869 mg/kg bw/day
Basis:
actual ingested
- No. of animals per sex per dose:
- 20 pregnant rats
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- No data
Examinations
- Maternal examinations:
- See result tables
- Ovaries and uterine content:
- See result tables
- Fetal examinations:
- See result tables
- Statistics:
- statistical significance difference of effects from controls were calculated at 5% level.
- Indices:
- No data
- Historical control data:
- No data
Results and discussion
Results: maternal animals
Maternal developmental toxicity
- Details on maternal toxic effects:
- Maternal toxic effects:yes
Details on maternal toxic effects:
Deaths (40%) and decreased bodyweight gain at 2869 mg/kg bw/day
Effect levels (maternal animals)
open allclose all
- Dose descriptor:
- NOAEL
- Effect level:
- 591 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Basis for effect level:
- other: maternal toxicity
- Dose descriptor:
- NOAEL
- Effect level:
- 591 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Basis for effect level:
- other: developmental toxicity
Results (fetuses)
- 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
Fetal abnormalities
- Abnormalities:
- not specified
Overall developmental toxicity
- Developmental effects observed:
- not specified
Any other information on results incl. tables
Maternal examinations:
- At 2869 mg/kg bw/day, maternal bodyweight decreased and several mothers (40%) died for a period of the treatment, but at 591 mg/kg bw/day, no changes were observed.
Fetal examinations:
- Delayed ossification of fetuses metacarpal bone and proximal phalanx at 2869 mg/kg bw/day was caused significantly, compared with the control group, but this was restored to normal within several weeks after birth.
- 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 bw/day.
Table 1: Body weight changes in pregnant rats treated orally with d-limonene
Dose (mg/kg bw) |
Gestational days |
Gain |
||||
0 |
9 |
12 |
16 |
20 |
||
Control |
214.80 ± 32.55 |
248.70 ± 28.92 |
265.60 ± 30.53 |
289.85 ± 35.01 |
325.30 ± 44.01 |
105.50 ± 29.67 |
591 |
221.25 ± 39.58 |
254.65 ± 41.16 |
264.80 ± 39.94 |
290.10 ± 38.37 |
325.60 ± 52.75 |
103.95 ± 19.38 |
2869 |
214.75 ± 4.57 |
258.75 ± 32.76
|
248.92 ± 26.27 |
263.17 ± 22.96 * |
305.00 ± 27.07 |
90.25 ± 22.38 |
* Significantly different from the control, P <0.05
Table 2: Effects of d-limonene on rat fetuses
Dose (mg/kg bw) |
Control |
591 |
2869 |
No. of mothers |
15 |
15 |
15 |
Mortality of mothers (%) |
0 |
0 |
40 |
No. of total implants |
12.73 ± 2.96 |
12.18 ± 3.65 |
10.44 ± 3.71 |
No. of dead fetuses |
0 |
0 |
0 |
No. of resorbed fetuses |
1.00 ± 1.10 |
1.47 ± 2.42 |
0.89 ± 0.73 |
No. of live fetuses |
176 |
162 |
87 |
Sex ratio (Male/Female) |
0.69 |
1.22 |
0.85 |
Fetuses body weight (g) Male |
3.71 ± 0.45 |
3.53 ± 0.35 |
3.73 ± 0.52 |
Female |
3.46 ± 0.44 |
3.38 ± 0.45 |
3.63 ± 0.40 |
Placental weight(g) Male |
0.49 ± 0.07 |
0.49 ± 0.10 |
0.48 ± 0.06 |
Female |
0.47 ± 0.07 |
0.46 ± 0.06 |
0.44 ± 0.05 |
Malformation External |
0 |
0 |
0 |
Visceral |
1 |
0 |
0 |
Table 3: Effects of d-limonene on skeletal development of rat fetuses
Dose (mg/kg bw) |
Control |
591 |
2869 |
No. of examined fetuses |
83 |
84 |
42 |
Variation Shortness of 13th rid |
1 |
0 |
0 |
Lumbar rid |
0 |
1 |
2 |
Asymmetry of sternebrae |
0 |
0 |
1 |
Ossification Delayed ossification of parietal bone |
2 |
0 |
0 |
Non-ossification of occipital bone
|
0 |
4 |
1 |
Non-ossification of parietal bone |
0 |
3 |
0 |
No. of ossified metacarpal bone |
7.69 ± 0.72 |
7.49 ± 0.84 |
6.97 ± 0.96 * |
No. of ossified proximal phalanx (Forelimb) |
2.48 ± 1.71 |
2.25 ± 1.81 |
0.55 ± 1.28 * |
No. of ossified metatarsal bone
|
7.98 ± 0.56 |
8.01 ± 011 |
8.00 ± 0 |
No. of ossified sternebraea |
5.47 ± 0.98 |
5.60 ± 0.71 |
5.52 ± 0.73 |
No. of ossified caudal vertebrae |
3.76 ± 0.64 |
3.80 ± 0.57 |
3.95 ± 0.68 |
* Significantly different from the control, P <0.05
Table 4: Body weight changes of postnatal rat offsprings born to mothers treated orally with d-limonene
Postnatal weeks |
Males |
Females |
||||
Dose (mg/kg bw) |
Dose (mg/kg bw) |
|||||
Control |
591 |
2869 |
Control |
591 |
2869 |
|
0 |
5.19 ± 0.55 |
5.46 ± 0.52 |
4.79 ± 0.46 |
4.93 ± 0.62 |
5.09 ± 0.68 |
4.89 ± 0.66 |
1 |
13.06 ± 1.50 |
12.49 ± 0.99 |
10.62 ± 1.54 * |
12.82 ± 1.59 |
12.22 ± 1.07 |
10.66 ± 1.84 |
2 |
26.06 ± 3.12 |
24.86 ± 2.74 |
22.67 ± 5.05 * |
25.88 ± 3.35 |
24.31 ± 2.42 |
22.72 ±.3.92 |
3 |
41.91 ± 5.89 |
39.55 ± 5.14 |
40.77 ± 5.16 |
41.08 ± 5.59 |
38.56 ± 4.37 |
38.39 ± 4.96 |
4 |
73.12 ± 9.89 |
71.33 ± 8.87 |
67.67 ± 8.02 |
69.66 ± 9.43 |
67.38 ± 6.71 |
66.01 ± 9.29 |
5 |
122.32 ± 12.25 |
116.47 ± 12.78 |
112.77 ± 12.65 * |
109.57 ± 10.61 |
107.58 ± 7.95 |
107.10 ± 13.34 |
6 |
176.04 ± 15.80 |
164.68 ± 16.69 |
163.11 ± 17 .85 * |
141.39 ± 10.54 |
140.11 ± 9.40 |
139.45 ± 14.22 |
7 |
235.52 ± 17.72 |
222.43 ± 18.57 |
213.64 ± 20.10 * |
173.06 ± 8.89 |
169.65 ± 11.13 |
167.84 ± 15.86 |
* Significantly different from the control, P <0.05
Table 5: Effects of d-limonene on postnatal development of the rats
Dose (mg/ kg bw) |
Days of postnatal development |
|||||
Opening of the ear-shell |
Coating with |
Odontiasis |
Opening of the eyelid |
Descending of the testis |
Opening of the vaginal orifice |
|
Control |
2.55 ± 0.76 |
5.51 ± 0.91 |
10.1 ± 0.96 |
14.83 ± 0.55 |
22.5 ± 1.30 |
35.6 ± 2.50 |
591 |
2.09 ± 0.82 |
6.00 ± 0 |
10.4 ± 0.71 |
15.00 ± 0.76 |
21.6 ± 1.39 |
35.5 ± 1.75 |
2869 |
2.41 ± 0.49 |
8.50 ±0.50 |
10.4 ± 1.85 |
15.14 ± 0.75 |
21.27 ± 0.57 |
35.93 ± 2.20 |
Table 6: Effects of d-limonene on development of rat offsprings
Dose (mg/kg) |
Control |
591 |
2869 |
No. of mothers |
5 |
5 |
5 |
Mortality of mothers |
0 |
0 |
40 |
No. of offspring from birth to the 7th week 0 |
61 |
65 |
33 |
1 |
53 |
63 |
30 |
2 |
53 |
63 |
30 |
3 |
53 |
63 |
28 |
4 |
53 |
63 |
28 |
5 |
53 |
63 |
28 |
6 |
53 |
63 |
28 |
7 |
53 |
63 |
28 |
External abnormality |
0 |
0 |
0 |
No. of total implants |
13.6 ± 3.1 |
14.8 ± 1.7 |
13.7 ± 1.7 |
No. of dead fetuses at birth |
4 |
4 |
5 |
Parturient rate |
95 |
92 |
93 |
Weaning rate |
89 |
97 |
85 |
Table 7: Absolute organ weights of postnatal rat offsprings born to mothers treated orally with d-limonene
Sex |
Dose (mg/kg bw) |
No. of offsprings. |
Final BW (g) |
Pituitary (mg) |
Thyroids (mg) |
Thymus (g) |
Lungs (g) |
Heart (g) |
Spleen (g) |
Kidneys (g) |
Liver (g) |
Adrenals (g) |
Testes (g) or Ovaries (mg) |
Male |
Control |
27 |
235.5 ± 17.7 |
10.04 ± 1.95 |
14.06 ± 2.52 |
0.77 ± 0.08 |
1.15 ± 0.10 |
0.82 ± 0.08 |
0.75 ± 0.11 |
2.18 ± 0.36 |
11.55 ± 1.14 |
38.85 ± 7.37 |
2.15 ± 0.17 |
591 |
29 |
222.4 ± 18.6 |
9.58 ± 4.84 |
13.12 ± 2.77 |
0.72 ± 0.09 |
1.10 ± 0.11 |
0.81 ± 0.08 |
0.69 ± 0.08 |
2.10 ± 0.20 |
11.24 ± 1 .49 |
36.77 ± 6.93 |
2.13 ± 0.28 |
|
2869 |
11 |
213.6 ± 20.1 |
9.69 ± 0.65 |
14.41 ± 3.60 |
0.66 ± 0.08 * |
1.19 ± 0.17 |
0.80 ± 0.07 |
0.63 ± 0.07 * |
2.23 ± 0.38 |
11.64 ± 1.64 |
43.23 ± 10.91 |
2.18 ± 0.14 |
|
Female |
Control |
25 |
173.1 ± 8.9 |
11.18 ± 3.15 |
12.26 ± 1.32 |
0.59 ± 0.08 |
0.97 ± 0.11 |
0.66 ± 0.07 |
0.52 ± 0.06 |
1.72 ± 0.22 |
8.88 ± 0.85 |
45.51 ± 8.01 |
77.24 ± 22.01 |
591 |
34 |
169.7 ± 11.7 |
10.05 ± 3.34 |
11.57 ± 1.62 |
0.54 ± 0.07 |
0.96 ± 0.07 |
0.67 ± 0.05 |
0.50 ± 0.06 |
1.60 ± 0.15 * |
8.16 ± 0.85 |
46.56 ± 8.45 |
85.84 ± 42.52 * |
|
2869 |
17 |
167.8 ± 15.9 |
9.95 ± 1.87 |
12.31 ± 1.80 |
0.51 ± 0.07 * |
0.94 ± 0.10 |
0.62 ± 0.06 |
0.44 ± 0.04 * |
1.62 ± 0.17 * |
8.50 ± 0.58 |
47.15 ± 6.63 |
63.15 ± 7.99 |
* Significantly different from the control, P <0.05
Table 8: Relative organ weights per 100 g body weights of postnatal rat offsprings born to mothers treated orally with d-limonene
Sex |
Dose (mg/kg bw) |
No. of offsprings. |
Final BW (g) |
Pituitary (mg/100 g) |
Thyroids (mg/100 g) |
Thymus (mg/100 g) |
Lungs (mg/100 g) |
Heart (mg/100 g) |
Spleen (mg/100 g) |
Kidneys (g/100 g) |
Liver (g/100 g) |
Adrenals (mg/100 g) |
Testes or Ovaries (mg/100 g) |
Male |
Control |
27 |
235.5 ± 17.7 |
4.31 ± 0.78 |
5.98 ± 0.99 |
0.33 ± 0.04 |
0.48 ± 0.04 |
0.36 ± 0.03 |
0.31 ± 0.05 |
0.93 ± 0.08 |
4.89 ± 0.36 |
16.49 ± 2.71 |
0.90 ± 0.04 |
591 |
29 |
222.4 ± 18.6 |
4.02 ± 0.50 |
5.93 ± 0.86 |
0.33 ± 0.04 |
0.49 ± 0.04 |
0.37 ± 0.04 |
0.33 ± 0.09 |
0.95 ± 0.07 |
5.10 ± 0.37 |
16.39 ± 2.53 |
0.95 ± 0.08 * |
|
2869 |
11 |
213.6 ± 20.1 |
4.23 ± 0.43 |
5.93 ± 0.66 |
0.28 ± 0.03 * |
0.51 ± 0.05 |
0.35 ± 0.02 |
0.27 ± 0.02 * |
0.96 ± 0.06 |
5.03 ± 0.27 |
17.23 ± 2.26 |
0.95 ± 0.09 |
|
Female |
Control |
25 |
173.1 ± 8.9 |
6.09 ± 1.08 |
7.08 ± 0.85 |
0.34 ± 0.05 |
0.54 ± 0.04 |
0.38 ± 0.04 |
0.30 ± 0.04 |
0.99 ± 0.12 |
5.14 ± 0.42 |
26.38 ± 4.71 |
47.94 ± 9.78 |
591 |
34 |
169.7 ± 11.7 |
5.82 ± 0.81 |
6.85 ± 0.96 |
0.32 ± 0.04 |
0.54 ± 0.12 |
0.40 ± 0.03 |
0.30 ± 0.03 |
0.95 ± 0.07 |
4.83 ± 0.37 |
27.61 ± 3.76 |
46.74 ± 10.76 |
|
2869 |
17 |
167.8 ± 15.9 |
6.27 ± 1.90 |
7.31 ± 0.90 |
0.31 ± 0.03 * |
0.57 ± 0.08 |
0.37 ± 0.03 |
0.27 ± 0.04 * |
0.94 ± 0.06 |
5.14 ± 0.33 |
26.75 ± 2.93 |
36.89 ± 4.25 * |
* Significantly different from the control, P <0.05
Applicant's summary and conclusion
- Conclusions:
- Under the test conditions, the NOAEL for maternal toxicity was considered to be 591 mg/kg bw/day based on the deaths and decreased bodyweight gain. The NOAEL for fetal toxicity was considered to be 591 mg/kg bw/day based on the delayed skeletal formation and decreased bodyweight gain.
- Executive summary:
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 suspended with 1% gum-arabic solution for 7 days from Day 9 to 15 of gestation. Bodyweight of pregnant rats were recorded on Days 0, 9, 12, 16 and 20 during organogenesis. Caesarean sections were performed and the number of dead, live or resorbed fetuses, sex ratio and number of implantation sites were recorded. Fetuses were weighed and examined for external, visceral and skeletal malformations. Number of live offsprings, gross differentiation and organ weights of offsprings were recorded until postnatal week 7.
At 2869 mg/kg bw/day, maternal bodyweight decreased and several mothers (40%) died for a period of the treatment, but at 591 mg/kg bw/day, no changes were observed. Delayed ossification of fetuses metacarpal bone and proximal phalanx at 2869 mg/kg bw/day was caused significantly, compared with the control group, but this was restored to normal within several weeks after birth. 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.
Under the test conditions, the NOAEL for maternal toxicity was considered to be 591 mg/kg bw/day based on the deaths and decreased bodyweight gain. The NOAEL for fetal toxicity was considered to be 591 mg/kg bw/day based on the delayed skeletal formation and decreased bodyweight gain.
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