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EC number: 701-299-7 | CAS number: -
- 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
- Study period:
- 2016-03-15 - 2016-04-07
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 017
- Report date:
- 2017
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- GLP compliance:
- yes (incl. QA statement)
- Limit test:
- no
Test material
- Reference substance name:
- Oligomerisation and alkylation reaction products of 2-phenylpropene and phenol
- EC Number:
- 700-960-7
- Molecular formula:
- not applicable
- IUPAC Name:
- Oligomerisation and alkylation reaction products of 2-phenylpropene and phenol
- Test material form:
- liquid: viscous
- Details on test material:
- - Manufacturers identification: Novares LA 300
- Substance type: organic
- Test material is 'Oligomerisation and alkylation reaction products of 2-phenylpropene and phenol' (OAPP), EC list number 700-960-7 (assigned manually to validated substances from inquiries by ECHA). Originally the substance phenol, methylstyrenated, CAS No. 68512-30-1, EC No. 270-966-8 was submitted for registration. Subsequent to substance validation, the identity of the substance was changed by ECHA.
- for additional information see respective study record
1
- Specific details on test material used for the study:
- - Name of test material (as cited in study report): Oligomerisation and alkylation reaction products of 2-phenylpropene and phenol (OAPP)
- Source and lot/batch No.of test material: RÜTGERS Novares GmbH, batch No. 38900
- Expiry date: 2017-02-13
- Composition of test material: composition is specified in IUCLID Sect. 13 - Assessment reports under Certificate of Analysis_Novares LA 300_phenol, methylstyrenated
- Stability under test conditions: found to be stable for 8 days (no longer observation)
- Storage condition of test material: room temperature, exclusion of light
Test animals
- Species:
- rat
- Strain:
- Wistar
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Laboratories, Research Models and Services, Germany GmbH, D-97633, Sulzfeld, from SPF colony
- Age at study initiation: 11 weeks old at mating
- Weight at study initiation: 186 - 229 g (females)
- Fasting period before study: no
- Housing: Standard laboratory conditions; individual housing
- Diet: ad libitum
- Water: ad libitum
- Acclimation period: at least 5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 19.9 - 23.9 °C
- Humidity (%): 40 - 53
- Air changes (per hr): 15 - 20
- Photoperiod (hrs dark / hrs light): 12 / 12
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- corn oil
- Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- According to CiToxLAB validation study, code 15/094-316AN, the test item is stable in the vehicle in the concentration range of 10 to 250 mg/mL for at least 8 days when stored at room temperature.
- Details on mating procedure:
- - Impregnation procedure: cohoused
- If cohoused:
- M/F ratio per cage: 1/1
- Length of cohabitation: approx. 2 h each event
- Proof of pregnancy: sperm in vaginal smear referred to as day 0 of pregnancy (GD0)
- Any other deviations from standard protocol: - Duration of treatment / exposure:
- from GD6 to GD19
- Frequency of treatment:
- 1x/d
- Duration of test:
- 20 d
Doses / concentrationsopen allclose all
- Dose / conc.:
- 60 mg/kg bw/day
- Dose / conc.:
- 150 mg/kg bw/day
- Dose / conc.:
- 300 mg/kg bw/day
- No. of animals per sex per dose:
- pregnant rats: 21 (control), 23 (low), 24 (mid), 23 (high)
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale: Maternal toxicity at 300 mg/kg bw/day (evident in decreased corrected body-weight gain and decreased food consumption).
- Rationale for animal assignment (if not random): The sperm-positive females were allocated to each experimental group (on each mating day) in such a way that the group averages of the body weight were as similar as possible.
- Dosage: Volume 3 mL/kg bw. The individual volume of the treatment was based on the most recent individual body weight of the animals.
Examinations
- Maternal examinations:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: 2x/d (working day)
- Cage side observations checked in Appendix 3.1 were included.
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: 1x/d (GD6), then 1x/wk
BODY WEIGHT: Yes
- Time schedule for examinations: on GD 0, 3, 6, 8, 10, 12, 14, 16, 18 and 20
FOOD CONSUMPTION: Yes
- Food consumption for each animal determined and mean daily diet consumption calculated as g food/kg body weight/day: yes
- Compound intake calculated as time-weighted averages from the consumption and body weight gain data: no (gavage)
POST-MORTEM EXAMINATIONS: Yes
- Sacrifice on gestation day 20
- Organs examined: gross pathology
OTHER: Gravid uterine weight - Ovaries and uterine content:
- The ovaries and uterine content was examined after termination: Yes
Examinations included:
- Gravid uterus weight: yes
- Number of corpora lutea: yes
- Number of implantations: yes
- Number of early resorptions: yes
- Number of late resorptions: yes
- Other: - Fetal examinations:
- - External examinations: yes; all per litter
- Soft tissue examinations: yes; half per litter
- Skeletal examinations: yes; half per litter
- Head examinations: yes; half per litter - Statistics:
- The statistical evaluation of data* was performed with the program package SPSS PC+4.0 (SPSS Hungary Kft, Budapest) or SAS 9.2 in the case of Provantis 9, by an appropriate statistical method (Bartlett, ANOVA and Duncan, Kruskal-Wallis and Mann-Whitney U tests, Chi2) using the litter as the unit for data analysis. The homogeneity of variance between groups was checked by Bartlett`s homogeneity of variance test. Where no significant heterogeneity was detected a one-way analysis of variance (ANOVA) was made. If the obtained result was significant Duncan’s Multiple Range test was used to assess the significance of inter-group differences. Significant results with inter-group comparisons were further compared using Kruskal-Wallis, and Mann-Whitney U-tests.
- Indices:
- Maternal: Preimplantation loss: %, group mean / Postimplantation loss: %, group mean
Foetal: Sex distribution: %, group mean; External abnormalities/litter: %, group mean; Visceral abnormalities/litter: %, group mean; Skeletal abnormalities/litter: %, group mean - Historical control data:
- availabe for litter and external foetal data, as well as for visceral and skeletal malformations, provided in combination with respective results tables.
Total available HC data have been compiled in Appendix 6 of the results report.
Results and discussion
Results: maternal animals
General toxicity (maternal animals)
- Clinical signs:
- no effects observed
- Mortality:
- no mortality observed
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- There was no statistically significant difference in the development of total body weight across all groups (Report, Fig. 1). However, bw gain during the treatment period from GD6 - GD20 revealed some significance in the mid- and high-dose groups (decrease ~11 to ~12% vs. control, p<0.05). This trend became more prominent after correction for the uterus content: decrease in bw gain from GD6 - GD20 = ~50% and ~40%, respectively (p<0.01) (Report, Tab. 1 and Fig. 2).
See also: "Any other information on results" below, and Attached Document
---------------------------------------------------------------------------------------------------------------------------------
Table 1: Body weight changes during the study
---------------------------------------------------------------------------------------------------------------------------------
Dose (mg/kg bw/day) 0 60 150 300
Number of litters 21 23 24 23
--------------------------------------------------------------------------------------------------------------------------------
Body weight gain GD6-20
(g) Mean 77.9 74.5 68.5* 69.3* DN
SD 12.64 11.77 11.08 13.52
% - -4.3 -12.1 -11.0
............................................................................................................................................................................
Body weight gain GD0-20
(g) Mean 97.2 93.6 87.8 90.0 NS
SD 13.71 14.68 13.33 13.44
% - -3.8 -9.8 -7.4
.............................................................................................................................................................................
Corrected net body weight gain
GD6-20
(g) Mean 20.62 18.83 10.25** 12.35* U
SD 8.40 6.10 11.00 10.64
% - -8.7 -50.3 -40.1
............................................................................................................................................................................
Corrected body weight gain
GD0-20
(g) Mean 40.00 37.87 29.54 33.13 NS
SD 10.07 6.61 12.56 10.44
% - -5.3 -26.1 -17.2
------------------------------------------------------------------------------------------------------------------------------------
*= p<0.05, **= p<0.015,
NS=Not Significant, DN=Duncan’s multiple range test, U = Mann-Whitney U-test - Food consumption and compound intake (if feeding study):
- effects observed, treatment-related
- Description (incidence and severity):
- The reduction in the food intake in the mid- and high-dose groups - though overall small and without clear dose-response - became more marked from the time of dosing on GD6 and thus is consistent with the concomittant decreases in the corrected body-weight gains (comp. Report, Fig. 3 and 4). Therefore, these effects on food intake are ascribed to treatment (see Attached document).
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- 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 examined
- Gross pathological findings:
- no effects observed
- Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- not examined
- Histopathological findings: neoplastic:
- not examined
- Other effects:
- not specified
Maternal developmental toxicity
- Number of abortions:
- no effects observed
- Description (incidence and severity):
- See "Any other information", Table 2
- Pre- and post-implantation loss:
- no effects observed
- Description (incidence and severity):
- See "Any other information", Table 2
- Total litter losses by resorption:
- no effects observed
- Description (incidence and severity):
- See "Any other information", Table 2
- Early or late resorptions:
- no effects observed
- Description (incidence and severity):
- See "Any other information", Table 2
- Dead fetuses:
- no effects observed
- Description (incidence and severity):
- See "Any other information", Table 2
- Changes in pregnancy duration:
- not examined
- Description (incidence and severity):
- Pregnancy was terminated on GD19.
- Changes in number of pregnant:
- effects observed, non-treatment-related
- Description (incidence and severity):
- Number of non-pregnant females: 2/24 (control); 1/24 (low); 0/24 (mid), and 1/24 (high)
- Other effects:
- not specified
- Details on maternal toxic effects:
- Significant treatment-related decreases in food consumption and in body-weight gain (without uterine weight) after dosage of 150 and 300 mg/kg bw/d from GD6 to GD19, considered adverse but without toxic manifestation.
Effect levels (maternal animals)
open allclose all
- Key result
- Dose descriptor:
- NOEL
- Effect level:
- 60 mg/kg bw/day
- Based on:
- test mat.
- Basis for effect level:
- other: based on absence of any test item-related effect
- Key result
- Dose descriptor:
- LOAEL
- Effect level:
- 150 mg/kg bw/day
- Based on:
- test mat.
- Basis for effect level:
- body weight and weight gain
- food consumption and compound intake
Maternal abnormalities
- Key result
- Abnormalities:
- effects observed, treatment-related
- Localisation:
- not specified
- Description (incidence and severity):
- reduced body-weight gain associated with suppressed food intake
Results (fetuses)
- Fetal body weight changes:
- no effects observed
- Description (incidence and severity):
- The weight of viable foetuses per litter in the Low-, Mid- and High-dose groups (60, 150 and 300 mg/kg bw/day, respectively) did not differ significantly from the control mean value. In any dose-group, the total number of retarded foetuses (with a weight of < the concurrent control mean minus 2 S.D.) as well as the number of affected litters was not significantly higher than the untreated control (see "Any other information", Table 3).
- Reduction in number of live offspring:
- no effects observed
- Description (incidence and severity):
- The mean number of viable foetuses was comparable with the control mean (see "Any other information", Table 2 and 3).
- Changes in sex ratio:
- no effects observed
- Description (incidence and severity):
- There was no toxicologically significant difference in the sex distribution of foetuses between the control and treatment groups (see "Any other information", Table 3).
- Changes in litter size and weights:
- no effects observed
- Description (incidence and severity):
- See "Any other information", Table 3
- Changes in postnatal survival:
- not examined
- External malformations:
- no effects observed
- Description (incidence and severity):
- No statistically significant differences were observed in these examined parameters of any test item-treated groups when compared to the negative (vehicle) control (see "Any other information on results", Table 4).
- Skeletal malformations:
- no effects observed
- Description (incidence and severity):
- All of the skeletal findings correspond to the current historical control (HC) or the concurrent study control data, or were considered to be spontaneous events unrelated to treatment (see "Any other information on results", Table 5).
- Visceral malformations:
- no effects observed
- Description (incidence and severity):
- All abnormalities observed at visceral examination in this study were considered incidental findings, consistent with the concurrent study control data and with historical control (HC) data, spontaneous events unrelated to treatment (see "Any other information on results", Table 6).
- Other effects:
- not specified
- Details on embryotoxic / teratogenic effects:
- no treatment-related effects observed (see under "Any other inormation on results").
Effect levels (fetuses)
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 300 mg/kg bw/day
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: absence of any adverse effect
- Remarks on result:
- other: highest dose tested
Fetal abnormalities
- Key result
- Abnormalities:
- no effects observed
Overall developmental toxicity
- Key result
- Developmental effects observed:
- no
Any other information on results incl. tables
Table 1 (Report Table 1): Body weight changes during the study
Concentration |
Dose (mg/kg bw/day) |
||||
0 |
60 |
150 |
300 |
||
Number of animals |
21 |
23 |
24 |
23 |
|
Body weight gain D06-20 (g) |
Mean |
77.9 |
74.5 |
68.5* (DN) |
69.3* (DN) |
SD |
12.64 |
11.77 |
11.08 |
13.52 |
|
% |
- |
-4.3 |
-12.1 |
-11.0 |
|
Body weight gain D0-20 (g) |
Mean |
97.2 |
93.6 |
87.8 |
90.0 |
SD |
13.71 |
14.68 |
13.33 |
13.44 |
|
% |
- |
-3.8 |
-9.8 |
-7.4 |
|
Corrected body weight gain |
Mean |
20.62 |
18.83 |
10.25** (U) |
12.35* (U) |
SD |
8.4 |
6.1 |
11 |
10.64 |
|
% |
- |
-8.7 |
-50.3 |
-40.1 |
|
Corrected body weight gain |
Mean |
40 |
37.87 |
29.54 |
33.13 |
SD |
10.07 |
6.61 |
12.56 |
10.44 |
|
% |
- |
-5.3 |
-26.1 |
-17.2 |
*= p<0.05, **= p<0.01, NS=Not Significant, DN=Duncan’s multiple range test, U = Mann-Whitney U-test.
Table 2 (Report Table 3): Summary of the intrauterine evaluation
Parameters |
Dose (mg/kg bw/day) |
|||
0 |
60 |
150 |
300 |
|
Number of evaluated dams |
21 |
23 |
24 |
23 |
Mean number of corpora lutea |
11.29 |
10.83 |
11.29 |
11.30 |
Mean number of implantations |
10.48 |
10.04 |
10.63 |
10.65 |
Preimplantation loss, mean |
0.81 |
0.78 |
0.67 |
0.65 |
Preimplantation loss (%), mean |
6.43 |
6.96 |
5.83 |
5.83 |
Early embryonic loss, mean |
0.24 |
0.39 |
0.08 |
0.43 |
Early embryonic loss (%), mean |
2.43 |
4.17 |
1.00 |
4.43 |
Late embryonic loss, mean |
0.00 |
0.04 |
0.00 |
0.09 |
Late embryonic loss (%), mean |
0.00 |
0.48 |
0.00 |
0.70 |
Dead foetuses, mean |
0.00 |
0.00 |
0.04 |
0.00 |
Dead foetuses (%), mean |
0.00 |
0.00 |
0.30 |
0.00 |
Postimplantation loss, mean |
0.24 |
0.43 |
0.13 |
0.52 |
Postimplantation loss (%), mean |
2.43 |
4.65 |
1.29 |
5.13 |
Total intrauterine mortality, mean |
1.05 |
1.22 |
0.79 |
1.13 |
Total intrauterine mortality (%), mean |
8.71 |
11.39 |
7.04 |
10.17 |
Viable foetuses, mean |
10.24 |
9.61 |
10.50 |
10.13 |
Notes:
1. No statistically significant differences were observed in these examined parameters of any test item-treated groups when compared to the negative (vehicle) control.
2. For calculation of the relative values (shown as %), the relative (%) value was calculated for each litter, then the mean value of those individual values was taken.
3. Data were rounded off to two decimal places.
Table 3 (Report Table 4): Examination of viable foetuses
Parameters |
Dose (mg/kg bw/day) |
|||
0 |
60 |
150 |
300 |
|
Number of examined litters |
21 |
23 |
24 |
24 |
Viable foetuses, mean |
10.24 |
9.61 |
10.50 |
10.13 |
Male foetuses, mean |
4.90 |
4.26 |
4.79 |
4.70 |
Female foetuses, mean |
5.33 |
5.35 |
5.71 |
5.43 |
Total number of foetuses |
215 |
221 |
252 |
233 |
Total number of male foetuses |
103 |
98 |
115 |
108 |
Total number of female foetuses |
112 |
123 |
137 |
125 |
Mean foetal weight / litter (g) |
3.373 |
3.442 |
3.329 |
3.433 |
Number of foetuses with retarded body weight |
8 |
1*CH |
11 |
9 |
Number of affected litters |
6 |
1*CH |
7 |
7 |
*statistically significant at p<0.05, CH = Chi square test
Table 4 (Report Table 5): Summary table of the external abnormalities
Parameter |
Control |
Dose (mg/kg bw/day) |
HC data |
||||
60 |
150 |
300 |
|||||
Total number of examined litters |
21 |
23 |
24 |
23 |
485 |
||
Total number of examined foetuses |
215 |
221 |
252 |
233 |
4955 |
||
Total number of intact (normal) foetuses |
215 |
221 |
251 |
233 |
-- |
||
Total number of foetuses / litters |
0 / 0 |
0 / 0 |
0 / 0 |
0 / 0 |
-- |
||
Total number of foetuses / litters |
0 / 0 |
0 / 0 |
1 / 1 |
0 / 0 |
-- |
||
External malformations |
|||||||
No external variations were recorded |
|||||||
External variations |
|||||||
Foetus, pale |
Litter |
n |
0 |
0 |
1 |
0 |
1 |
% |
0.0 |
0.0 |
4.2 |
0.0 |
0.2 |
||
Foetal |
n |
0 |
0 |
1 |
0 |
1 |
|
% |
0.000 |
0.000 |
0.396 |
0.000 |
0.020 |
Notes: Numbers represent the number (n) or ratio (%) of abnormalities.Notes: Numbers represent the number (n) or ratio (%) of abnormalities.
HC: historical control
No statistically significant differences were observed in these examined parameters of any test item-treated groups when compared to the negative (vehicle) control.
Table 5 (Report Table 7): Summary table of the skeletal abnormalities
Parameter |
Control |
Dose (mg/kg bw/day) |
HC data |
||||
60 |
150 |
300 |
|||||
Total number of examined litters |
21 |
23 |
24 |
23 |
485 |
||
Total number of examined foetuses |
107 |
111 |
127 |
116 |
2467 |
||
Total number of intact (normal) foetuses |
99 |
97 |
117 |
111 |
-- |
||
Total number of foetuses / litters |
1 / 1 |
1 / 1 |
0 / 0 |
1 / 1 |
-- |
||
Total number of foetuses / litters |
7 / 7 |
13 / 11 |
10 / 7 |
4 / 4 |
-- |
||
Skeletal malformations |
|||||||
Pelvic girdle, mal-positioned# |
Litter |
n |
1 |
0 |
0 |
1 |
2 |
% |
4.8 |
0.0 |
0.0 |
4.3 |
0.4 |
||
Foetal |
n |
1 |
0 |
0 |
1 |
2 |
|
% |
0.935 |
0.000 |
0.000 |
0.862 |
0.081 |
||
Malformed vertebrae, (Hemivertebrae) |
Litter |
n |
0 |
1 |
0 |
0 |
0 |
% |
0.0 |
4.3 |
0.0 |
0.0 |
0.0 |
||
Foetal |
n |
0 |
1 |
0 |
0 |
0 |
|
% |
0.000 |
0.901 |
0.000 |
0.000 |
0.000 |
||
Skeletal variations |
|||||||
Skull, 2 or more bones incomplete ossification |
Litter |
n |
3 |
2 |
1 |
2 |
326 |
% |
14.3 |
8.7 |
4.2 |
8.7 |
67.2 |
||
Foetal |
n |
4 |
2 |
3 |
2 |
474 |
|
% |
3.738 |
1.802 |
2.362 |
1.724 |
19.214 |
||
Ossified sternebra (3 or less) |
Litter |
n |
1 |
1 |
1 |
0 |
37 |
% |
4.8 |
4.3 |
4.2 |
0.0 |
7.6 |
||
Foetal |
n |
1 |
1 |
1 |
0 |
46 |
|
% |
0.935 |
0.901 |
0.787 |
0.000 |
1.865 |
||
Xiphoid cartilage, hole |
Litter |
n |
1 |
1 |
0 |
1 |
11 |
% |
4.8 |
4.3 |
0.0 |
4.3 |
2.3 |
||
Foetal |
n |
1 |
1 |
0 |
1 |
14 |
|
% |
0.935 |
0.901 |
0.000 |
0.862 |
0.567 |
||
Fontanelle, large |
Litter |
n |
0 |
0 |
1 |
0 |
2 |
% |
0.0 |
0.0 |
4.2 |
0.0 |
0.4 |
||
Foetal |
n |
0 |
0 |
1 |
0 |
2 |
|
% |
0.000 |
0.000 |
0.787 |
0.000 |
0.081 |
||
Rib, wavy, marked |
Litter |
n |
1 |
0 |
0 |
0 |
149 |
% |
4.8 |
0.0 |
0.0 |
0.0 |
30.7 |
||
Foetal |
n |
1 |
0 |
0 |
0 |
243 |
|
% |
0.935 |
0.000 |
0.000 |
0.000 |
9.850 |
||
Vertebra, dumbbell or asymmetric ossification (2 or more) |
Litter |
n |
1 |
6 |
4 |
1 |
73 |
% |
4.8 |
26.1 |
16.7 |
4.3 |
15.1 |
||
Foetal |
n |
1 |
7*CH |
4 |
1 |
79 |
|
% |
0.935 |
6.306 |
3.150 |
0.862 |
3.202 |
Notes: Numbers represent the number (n) or ratio (%) of abnormalities.
HC: historical control
*statistically significant at p<0.05, CH = Chi square test
Table 6 (Report Table 6): Summary table of the visceral abnormalities
Parameter |
Control |
Dose (mg/kg bw/day) |
HC data |
||||
60 |
150 |
300 |
|||||
Total number of examined litters |
21 |
23 |
24 |
23 |
485 |
||
Total number of examined foetuses |
108 |
110 |
125 |
117 |
2484 |
||
Total number of intact (normal) foetuses |
104 |
108 |
121 |
115 |
-- |
||
Total number of foetuses / litters |
1 / 1 |
0 / 0 |
1 / 1 |
0 / 0 |
-- |
||
Total number of foetuses / litters |
3 / 3 |
2 / 2 |
3 / 3 |
2 / 2 |
-- |
||
Visceral malformations |
|||||||
A-V septum, defect |
Litter |
n |
1 |
0 |
0 |
0 |
0 |
% |
4.8 |
0.0 |
0.0 |
0.0 |
0.0 |
||
Foetal |
n |
1 |
0 |
0 |
0 |
0 |
|
% |
0.926 |
0.000 |
0.000 |
0.000 |
0.000 |
||
Great arteries, transposition |
Litter |
n |
0 |
0 |
1 |
0 |
0 |
% |
0.0 |
0.0 |
4.2 |
0.0 |
0.0 |
||
Foetal |
n |
0 |
0 |
1 |
0 |
0 |
|
% |
0.000 |
0.000 |
0.800 |
0.000 |
0.000 |
||
Visceral variations |
|||||||
Thymic cord |
Litter |
n |
2 |
0 |
0 |
1 |
55 |
% |
9.5 |
0.0 |
0.0 |
4.3 |
11.3 |
||
Foetal |
n |
2 |
0 |
0 |
1 |
66 |
|
% |
1.852 |
0.000 |
0.000 |
0.855 |
2.657 |
||
Renal papilla, small |
Litter |
n |
0 |
0 |
2 |
1 |
16 |
% |
0.0 |
0.0 |
8.3 |
4.3 |
3.3 |
||
Foetal |
n |
0 |
0 |
2 |
1 |
18 |
|
% |
0.000 |
0.000 |
1.653 |
0.855 |
0.725 |
||
Brachiocephalic trunk, short |
Litter |
n |
1 |
1 |
1 |
0 |
35 |
% |
4.8 |
4.3 |
4.2 |
0.0 |
7.2 |
||
Foetal |
n |
1 |
1 |
1 |
0 |
43 |
|
% |
0.926 |
0.909 |
0.800 |
0.000 |
1.731 |
||
Ureter convoluted |
Litter |
n |
0 |
1 |
0 |
0 |
3 |
% |
0.0 |
4.3 |
0.0 |
0.0 |
0.6 |
||
Foetal |
n |
0 |
1 |
0 |
0 |
3 |
|
% |
0.000 |
0.909 |
0.000 |
0.000 |
0.121 |
Notes: Numbers represent the number (n) or ratio (%) of abnormalities.
HC: historical control
No statistically significant differences were observed in these examined parameters of any test item-treated groups when compared to the negative (vehicle) control
#:Lumbar VI.- Sacral I. transverse processes, fused
Applicant's summary and conclusion
- Conclusions:
- Doses of ≥ 150 mg/kg bw/day of OAPP produced mild but significant maternal toxicity in pregnant Wistar rats. However, this was limited to a reduction in body-weight gain corrected for the uterine mass. Maternal growth retardation correlated with reduced food intake during the exposure period (GD6 through GD19). Prenatal adverse effects that could have been ascribed to the test-item were not observed at any dose level.
The maternal NOEL (No-observed-effect level) and LOAEL were 60 and 150 mg/kg bw/day, respectively, while the NOAEL for embryo- and foetotoxicity was 300 mg/kg bw/day, the highest dose tested, which proved to be maternally toxic.
- Executive summary:
In a GLP-conform guideline study on prenatal development according to OECD 414, oligomerisation and alkylation reaction products of 2-phenylpropene and phenol (OAPP) [EC-no. 700 -960 -7], administered daily by oral gavage to pregnant Hannover Wistar rats from gestation days GD6 to GD19, was associated with the following findings: In the Mid- and High-dose group (150 and 300 mg/kg bw/day), there was a reduction in maternal body-weight gain and corrected body-weight gain, as well as in food intake during Gestation Day 6 – 20. The differences were considered to be relatively mild signs of maternal toxicity. There was no evidence of any adverse maternal effects in the Low-dose group at 60 mg/kgbw/day.
There were no toxicologically significant differences or test item related-changes in the reproductive parameters examined up to and including 300 mg/kg bw/day. No foetal effects were seen at exteral, visceral and/or skeletal examination of foetuses in the study which could be related to the test-item administration.
In this study, from the observations made in the dams and their foetuses, the following no-observed-adverse-effect (NOAEL), low-observed-adverse effect (LOAEL) or no-observed-effect (NOEL) levels were derived:
LOAELmaternal toxicity: 150 mg/kg bw/day
NOELmaternal toxicity: 60 mg/kg bw/day
NOAELembryotoxicity: 300 mg/kg bw/day
NOAELfoetotoxicity: 300 mg/kg bw/day
NOAELteratogenecity: 300 mg/kg bw/day.
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