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EC number: 295-714-4 | CAS number: 92128-22-8
- 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
Developmental toxicity / teratogenicity
Administrative data
- Endpoint:
- developmental toxicity
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 010
- Report date:
- 2010
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 870.3700 (Prenatal Developmental Toxicity Study)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- other: Japanese MAFF guideline No. 8147 (2000, amended 2001)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- other: 2004/73/EEC (2004)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Limit test:
- yes
Test material
- Reference substance name:
- Fatty acids, tall-oil, compds. with N-[3-(dimethylamino)propyl]tall-oil amides
- EC Number:
- 295-714-4
- EC Name:
- Fatty acids, tall-oil, compds. with N-[3-(dimethylamino)propyl]tall-oil amides
- Cas Number:
- 92128-22-8
- Molecular formula:
- Not applicable (UVCB substance)
- IUPAC Name:
- Reaction products of tall-oil fatty acids and (3-aminopropyl)dimethylamine
- Test material form:
- liquid
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Wistar
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Harlan Netherlands B.V. (Horst, Netherlands)
- Age at study initiation: at least 12 weeks
- Weight at study initiation: females: 203-268 g
- Housing: individually
- Diet: ad libitum
- Water: ad libitum
- Acclimation period: at least 1 week
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20.2-21.4
- Humidity (%): 62-67
- Air changes (per hr): at least 10
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- corn oil
- Details on exposure:
- administration volume: 2 ml/kg bw
- Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Before the start of treatment, the suitability of the formulation was confirmed by the analysis of concentration and stability of dosage forms prepared in the same way as it was done in the study. Analyses were carried out before the start of the study. The respective analytical data confirmed that the formulations in corn oil at 5 to 500 mg/ml are stable at room temperature for at least 17 days. For content checks the concentrations of samples of control and each test item dosage formulation prepared were determined twice during the study.
- Details on mating procedure:
- The animals were mated by placing one female overnight into a Type IIIh cage together with one male rat. If sperm was detected in the vaginal smear taken on the morning following mating, this day was regarded as day 0 of gestation.
- Duration of treatment / exposure:
- day 6 to day 20 of gestation
- Frequency of treatment:
- once daily
- Duration of test:
- 21 days
Doses / concentrationsopen allclose all
- Dose / conc.:
- 100 mg/kg bw/day
- Dose / conc.:
- 300 mg/kg bw/day
- Dose / conc.:
- 1 000 mg/kg bw/day
- No. of animals per sex per dose:
- 25
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- DOSE SELECTION RATIONALE:
The dose levels were selected based on the results of a previous dose toleration study in rats with Zusatzmittel VP PU 1748 in which two rats received the limit dose of 1000 mg/kg orally once daily from day 6 to day 20 of gestation (Study number: T3074534). In this orientating study no indications for maternotoxicity or fetotoxicity occurred. In addition, an orientating systemic toxicity study was conducted in male and female rats in which the doses of 100, 300 and 1000 mg/kg Zusatzmittel VP PU 1748 were orally administered over approximately two weeks (Study number: T8079921). Some female animals at the high dose level of 1000 mg/kg showed histologically slight forestomach erosion and ulceration. Correspondingly, the NOAEL for female rats was 300 mg/kg Zusatzmittel VP PU 1748 in this orientating study.
Examinations
- Maternal examinations:
- - Clinical observations: appearance, behaviour, excretory products and mortality, from day 0-21 p.c. once daily
- Body weights: on day 0 p.c. and daily from day 6-21 p.c.
- Food consumption: from day 0-21 p.c.
- Gross pathological examination: at the time of cesarean section on day 21 p.c. - Ovaries and uterine content:
- The following parameters were determined and assessed at cesarean section on day 21 p.c.:
- Number of corpora lutea
- Number of implantations
- Uterine weights
- Individual weight and appearance of the placentas
- Number of early resorptions
- Number of late resorptions
- Number of dead fetuses
- Number of live fetuses - Fetal examinations:
- - Number of live fetuses
- Sex of live fetuses
- Individual weights of live fetuses
- External abnormalities (malformations/variations)
- Visceral abnormalities (malformations/variations)
- Skeletal and cartilage abnormalities (malformations/variations) - Statistics:
- - Dunnett test:
mean feed consumption, mean body weights, mean body weight gains, and mean corrected body weight gains, mean uterine weights, mean number of Corpora lutea, mean number of implantations, mean number of resorptions, mean number of postimplantation losses, total number of fetuses, mean number of live/dead fetuses, mean placental weights, mean litter weight, mean fetal weights, mean fetal weight of male/female fetuses.
- Fisher’s exact test with Bonferroni-Holm correction:
fertility and gestation rate, percentage of preimplantation losses per group, percentage of postimplantation losses or dead fetuses per group, percentage of total resorptions, early and late resorptions per group, percentage of sex of male and female fetuses per group, percentage of fetuses or litters with external, visceral, skeletal and cartilage abnormalities (malformations and variations) findings per group.
- Wilcoxon-Mann-Whitney test with Bonferroni-Holm correction:
percentage of preimplantation losses per female, percentag of postimplantation losses, resorptions or dead fetuses per female, percentage of fetuses or litters with external, visceral, skeletal and cartilage abnormalities (malformations and variations) per female. - 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:
One female of the mid dose group of 300 mg/kg died due to misapplication. Increased sialorrhea occurred in all study groups including the control group and with a dose-dependently increased incidence at the low dose and higher. Due to local irritating properties of the test substance a compound-relation is considered likely. A dose-dependent effect on body weight gain was induced at the mid dose of 300 mg/kg and higher. The body weight gain was slightly lower at the end of the treatment period at 300 mg/kg and distinctly lower already after start of treatment at the high dose of 1000 mg/kg. This impairment was related to body weight loss at 300 mg/kg (individual animals) and at 1000 mg/kg and markedly reduced feed intake at the high dose level during the whole treatment period. No substance related macroscopic findings were observed up to and including 1000 mg/kg.
Effect levels (maternal animals)
open allclose all
- Dose descriptor:
- NOAEL
- Remarks:
- general toxicity (systemic)
- Effect level:
- 100 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Basis for effect level:
- body weight and weight gain
- other: food intake
- Dose descriptor:
- NOAEL
- Remarks:
- general toxicity (local)
- Effect level:
- < 100 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Basis for effect level:
- clinical signs
- Remarks on result:
- other: increased sialorrhea (local irritating effect)
- Dose descriptor:
- NOAEL
- Remarks:
- maternal developmental toxicity
- Effect level:
- 1 000 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Basis for effect level:
- other: no treatment-related effects observed
Results (fetuses)
- Details on embryotoxic / teratogenic effects:
- Embryotoxic / teratogenic effects: yes
Details on embryotoxic / teratogenic effects:
The gestation rate, number of corpora lutea, postimplantation loss, litter size, fetal sex distribution, placental weights and placental appearance were not affected by treatment up to and including 1000 mg/kg. The spontaneous occurring slightly higher mean number of fetuses at the mid dose level of 300 mg/kg was consequently accompanied by marginally lower fetal body weight. Incidence of structural findings classified as malformations observed in this study at levels up to and including 1000 mg/kg was low and dose-relation was not evident. The types of fetal malformations are considered a representative sample of spontaneous malformations in the rat strain used. Thus treatment-relation for malformations was not evident up to an including 1000 mg/kg. Furthermore, no substance related fetal structural findings classified as external, visceral or cartilage variations were noted up to and including 1000 mg/kg. At the mid dose of 300 mg/kg and higher skeletal findings indicating a retarded ossification occurred. These changes were seen at the 300 mg/kg level together with incidentally higher litter size which may have contributed to the marginally retarded ossification. A further sign of a retarded fetal development was a reduced fetal weight at the high dose level of 1000 mg/kg. The more progressed ossification in sternebrae as well as the mandibular and the zygomatic bone at1000 mg/kg is considered toxicologically irrelevant as it is highly unlikely that more progressed and retarded ossification occurs simultaneously. In addition, the fused cartilage (processus spinosus) of the 10th and 11th thoracal vertebral arches noted without dose-dependence at the low dose of 100 mg/kg and higher is highly likely a spontaneous effect.
Effect levels (fetuses)
- Dose descriptor:
- NOAEL
- Remarks:
- fetal developmental toxicity
- Effect level:
- 100 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- not specified
- Basis for effect level:
- fetal/pup body weight changes
- other: skeletal findings (retarded ossification)
Fetal abnormalities
- Abnormalities:
- not specified
Overall developmental toxicity
- Developmental effects observed:
- not specified
Any other information on results incl. tables
Table 1: Mean Body Weight Gain (females during the treatment and gestation period) |
||||
Dose [mg/kg bw/day] |
0 |
100 |
300 |
1000 |
mean body weight gain [g] |
||||
days 6 - 20 p.c. |
98.1 |
100.5 |
91.0 |
61.2** |
days 0 - 21 p.c. |
134.1 |
141.5 |
130.8 |
91.7** |
days 15 – 18 p.c. |
35.9 |
34.2 |
27.0* |
25.2** |
days 18 – 21 p.c. |
35.1 |
35.6 |
30.3 |
23.1* |
corrected body weight gain [g] |
||||
days 6 - 21 p.c. |
20.3 |
23.0 |
16.0 |
-14.1** |
Statistically significant difference to control * p < =.05 and ** p < 0.01 |
Table 2: Mean Feed Intake |
||||
Dose [mg/kg bw/day] |
0 |
100 |
300 |
1000 |
Mean feed consumption [g/female/day] |
||||
days 0 - 3 p.c. |
20.7 |
20.8 |
21.8 |
21.1 |
days 3 - 6 p.c. |
22.4 |
23.2 |
23.9* |
22.7 |
days 6 - 9 p.c. |
20.7 |
22.1 |
21.7 |
16.0** |
days 9 - 12 p.c. |
22.8 |
22.7 |
22.3 |
18.0** |
days 12 - 15 p.c. |
22.5 |
23.7 |
23.4 |
17.3** |
days 15 - 18 p.c. |
25.7 |
25.8 |
24.7 |
18.9** |
days 18 - 20 p.c. |
24.5 |
25.3 |
21.5 |
18.4** |
days 6 - 21 p.c. |
23.2 |
23.9 |
22.9 |
17.7** |
days 0 - 21 p.c. |
22.7 |
23.4 |
22.9 |
18.9** |
Statistically significant difference to control * = p < 0.05 and ** = p < 0.01 |
Table 3: General Reproduction Data |
||||
Dose [mg/kg bw/day] |
0 |
100 |
300 |
1000 |
Number inseminated females (total): |
25 |
25 |
25 |
25 |
- Number died during gestation |
0 |
0 |
1a |
0 |
- Number delivered prematurely |
0 |
0 |
1b |
0 |
Number surviving females with defined day 0 p.c.: |
25 |
25 |
23 |
25 |
- Number not pregnant |
0 |
1c |
1c |
0 |
- Number surviving females pregnant |
25 |
24 |
22 |
25 |
- Number surviving females with viable fetuses |
25 |
24 |
22 |
25 |
- Number surviving females with total resorptions |
0 |
0 |
0 |
0 |
Values per female with viable fetuses: |
25 |
24 |
22 |
25 |
- Corpora lutea (mean) |
16.2 |
16.17 |
17.05d |
16.04 |
- Preimplantation loss (% per group) |
10.37 |
9.79 |
10.89d |
10.22 |
- Implantations (mean) |
14.52 |
14.58 |
15.13d |
14.40 |
a one female (no. 67) died |
Table 4: Gestation Rate |
|||
Dose |
Females with viable fetuses |
Females |
|
[mg/kg bw/day] |
N |
in % of Females with Implantations |
with Total Resorption |
0 |
25 |
100.0 |
0 |
100 |
24 |
100.0 |
0 |
300 |
22a |
100.0 |
0 |
1000 |
25 |
100.0 |
0 |
a female no. 67 (pregnant) died due to misapplication and one female (no. 75) with premature delivery was excluded from calculation |
Table 5: Mean Values for Parameters of Intrauterine Development |
||||
Dose [mg/kg bw/day] |
0 |
100 |
300 |
1000 |
Number of females |
||||
with implantations |
25 |
24 |
23a |
25 |
with viable fetuses |
25 |
24 |
23a |
25 |
Values per female: |
||||
placental weight in g (mean) |
0.67 |
0.68 |
0.68 |
0.67 |
number of live fetuses (mean) |
13.48 |
13.21 |
14.22 |
13.64 |
postimplantation loss(mean) |
1.04 |
1.38 |
0.91 |
0.76 |
% males |
50.15 |
47.00 |
48.01 |
46.33 |
fetal weight in g (mean) |
4.90 |
5.03 |
4.70 |
4.49** |
a including data on one female (no. 75) which delivered prematurely on day 21 p.c. Statistically significant difference to control ** = p < 0.01 |
Table 6: Fetal Malformations |
||||||
Malformation (N) |
Dose [mg/kg bw/day] |
|||||
|
0 |
100 |
300a |
1000 |
|
|
External malformations (Total): |
0 |
0 |
0 |
0 |
|
|
|
||||||
Visceral malformations (Total): |
1 |
1 |
1 |
2 |
|
|
- severely dilated renal pelvis |
1 |
1 |
0 |
2 |
|
|
- absent eyes |
0 |
0 |
1 |
0 |
|
|
|
|
|
|
|
|
|
Skeletal malformations (Total): |
|
|
|
|
|
|
- sternoschisis |
0 |
0 |
1 |
0 |
|
|
- supernumerary lumbar vertebra |
1 |
0 |
0 |
0 |
|
|
- fused thoracal vertebral bodies |
0 |
1 |
0 |
0 |
|
|
- absent ribs |
1 |
0 |
1 |
0 |
|
|
|
||||||
|
||||||
Number of fetuses per group (Total)b |
338 |
317 |
329 |
342 |
|
|
Number of fetuses with malformations |
3 |
2 |
3 |
2 |
|
|
Fetuses with malformations per group (%) |
0.89 |
0.63 |
0.91 |
0.58 |
|
|
|
||||||
Number of litters per group |
25 |
24 |
23 |
25 |
|
|
Number of litters with malformations |
3 |
2 |
3 |
2 |
|
|
Litters with malformations per group (%) |
12.0 |
8.3 |
13.0 |
8.0 |
|
|
a including fetal data on one female (no. 75) which delivered prematurely on day 21 p.c. b including dead fetuses (1, 0, 2, 1 in control, low, mid and high dose, respectively) |
Applicant's summary and conclusion
- Executive summary:
In a prenatal developmental toxicity study according to OECD TG 414 25 inseminated female Wistar rats each were treated orally by gavage with the test substance using corn oil as the vehicle. Females were treated from day 6 to day 20 of gestation with dosages of 0, 100, 300 and 1000 mg/kg bw/day, respectively. The fetuses were delivered by cesarean section on day 21 of gestation. Examinations were performed on general tolerance of the test compound by the females and possible effects on intrauterine development. Increased sialorrhea occurred in all study groups including the control group and with a dose-dependently increased incidence at the low dose and higher. Due to local irritating properties of the test substance a compound-relation is considered likely. A dose-dependent effect on body weight gain was induced at the mid dose of 300 mg/kg and higher. The body weight gain was slightly lower at the end of the treatment period at 300 mg/kg and distinctly lower already after start of treatment at the high dose of 1000 mg/kg. This impairment was related to body weight loss at 300 mg/kg (individual animals) and at 1000 mg/kg and markedly reduced feed intake at the high dose level during the whole treatment period. No substance related macroscopic findings were observed up to and including 1000 mg/kg. The gestation rate, number of corpora lutea, postimplantation loss, litter size, fetal sex distribution, placental weights and placental appearance were not affected by treatment up to and including 1000 mg/kg. The spontaneous occurring slightly higher mean number of fetuses at the mid dose level of 300 mg/kg was consequently accompanied by marginally lower fetal body weight. Incidence of structural findings classified as malformations observed in this study at levels up to and including 1000 mg/kg was low and dose-relation was not evident. The types of fetal malformations are considered a representative sample of spontaneous malformations in the rat strain used. Thus treatment-relation for malformations was not evident up to an including 1000 mg/kg. Furthermore, no substance related fetal structural findings classified as external, visceral or cartilage variations were noted up to and including 1000 mg/kg. At the mid dose of 300 mg/kg and higher skeletal findings indicating a retarded ossification occurred. These changes were seen at the 300 mg/kg level together with incidentally higher litter size which may have contributed to the marginally retarded ossification. A further sign of a retarded fetal development was a reduced fetal weight at the high dose level of 1000 mg/kg. The more progressed ossification in sternebrae as well as the mandibular and the zygomatic bone at 1000 mg/kg is considered toxicologically irrelevant as it is highly unlikely that more progressed and retarded ossification occurs simultaneously. In addition, the fused cartilage (processus spinosus) of the10th and 11th thoracal vertebral arches noted without dose-dependence at the low dose of 100 mg/kg and higher is highly likely a spontaneous effect. Summarizing and evaluating all data investigated the no-observed-adverse-effect level (NOAEL) for maternal toxicity (systemic effects) and developmental toxicity is 100 mg/kg bw/day. Regarding the maternal toxicity for local irritating effect (sialorrhea) the NOAEL is < 100 mg/kg bw/day. Thus, developmental toxicity occurs only in the presence of clear maternal toxicity.
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