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EC number: 701-396-4 | 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
Endpoint summary
Administrative data
Key value for chemical safety assessment
Effects on fertility
Description of key information
- 3-generation reproduction study (non-guideline study, RL2), rats, diet: no effects observed
Link to relevant study records
- Endpoint:
- three-generation reproductive toxicity
- Type of information:
- read-across from similar mixture/product
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Acceptable publication which meets basic scientific principles.
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- A three-generation reproduction study was conducted on polyglycerol polyricinoleate (PGPR) to investigate the potential adverse effects on reproduction. Breeding was conducted using a continuous breeding protocol in which pairs of animals were maintained until each female had produced five litters (or it became evident that breeding had ceased). This procedure was repeated over three generations. The main focus of the study design was to observe any effect on breeding. This study was conducted during the late 1950s/early1960s and the methods represented the state of the art which existed during this period. The study nevertheless allow an adequate assessment of the potential reproductive and chronic toxicity of PGPR.
- GLP compliance:
- no
- Limit test:
- yes
- Species:
- rat
- Strain:
- other: Colworth Wistar rats
- Details on species / strain selection:
- No details given.
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: breeding facility at the Unilever Colworth Laboratory, Sharnbrook, Bedford, UK
- Diet: commercial pelleted stock diet (Spital), ad libitum
- Water: ad libitum - Route of administration:
- oral: feed
- Vehicle:
- unchanged (no vehicle)
- Details on exposure:
- DIET PREPARATION
- Rate of preparation of diet (frequency): each week
- Mixing appropriate amounts with (Type of food): PGPR was incorporated into the ground diet first by hand followed by mixing in a mechanical mixer. - Details on mating procedure:
- - M/F ratio per cage: 1/1
- Length of cohabitation: One male and one female were cohoused until succesful mating was determined. The respective mating couples were maintained for 5 reproduction cycles or until such time as it became evident that breeding had ceased. - Analytical verification of doses or concentrations:
- no
- Details on analytical verification of doses or concentrations:
- No analytical verification conducted.
- Duration of treatment / exposure:
- Continuously with diet and via mother's milk.
- Frequency of treatment:
- Continuously with diet and via mother's milk.
- Details on study schedule:
- The first-generation parents (P0) were selected from five litters which were assigned randomly into two groups: a control (11 males and 17 females) and a treatment group fed 1.5% PGPR (six males and 13 females). All rats were weaned at 23 days and mated at 121 days. Breeding was continuous and the males were only separated from the females when it was apparent that the female was pregnant. In all instances the first litters were discarded after weaning and second-generation breeders (F1) were randomly selected (two males and two females) from each of the second and fourth litters. By selecting from two first-generation litters the number of animals was increased to 52 of each sex in the control and 32 of each sex in the PGPR group. The third-generation breeders (F2) were selected in a similar manner, by which the control and the PGPR groups were increased to 92 and 44 rats of each sex, respectively. The large control groups were considered necessary to get an indication of the variations in breeding results that occur within a normal breeding colony.
- Dose / conc.:
- 1.5 other: % (w/w)
- Dose / conc.:
- 2 000 mg/kg bw/day (nominal)
- Remarks:
- (the breeding females consumed PGPR at levels > 2 g/kg bw/day (based on a food intake level of up to 40 g/day during lactation and the inclusion of PGPR in the diet at the fixed level of 1.5%))
- No. of animals per sex per dose:
- - 1st generation (P0): 11 males / 17 females (control group); 6 males / 13 females (treatment group)
- 2nd generation (F1): 52 males / 52 females (control grooup); 32 males / 32 females (treatment group)
- 3rd generation (F2): 92 males / 92 females (contro group); 44 males / 44 females (treatment group) - Control animals:
- yes, plain diet
- Details on study design:
- - Dose selection rationale: The dietary level of 1.5% PGPR was chosen to provide an intake by the pregnant and lactating rat which was in excess of 150 times the intake of a person consuming 5 mg PGPR/kg bw/day.
- Positive control:
- No
- Parental animals: Observations and examinations:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: daily
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: daily
BODY WEIGHT: Yes
- Time schedule for examinations: Growth was monitored from weaning to mating during the first 4 months of each generation. The weights of the females were recorded at weaning and mating, while the weight of the males was recorded at weaning and day 65.
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study): Food intakes were not recorded in this study, but it has been shown in an earlier publication that levels of 5% PGPR in the diet has no effect on food intake.
- Oestrous cyclicity (parental animals):
- Not examined.
- Sperm parameters (parental animals):
- Not examined.
- Litter observations:
- PARAMETERS EXAMINED
The following parameters were examined in the 3 generations:
number of litters per dam, average litter size, average weaning weights of males and females, litters per group showing 100% survival and total survival (%) at day 21
- Postmortem examinations (parental animals):
- Not examined.
- Postmortem examinations (offspring):
- Not examined.
- Statistics:
- A Student's t-test was conducted in which the two groups were compared.
- Reproductive indices:
- No data.
- Offspring viability indices:
- No data.
- Clinical signs:
- no effects observed
- Mortality:
- no mortality observed
- Body weight and weight changes:
- no effects observed
- Food consumption and compound intake (if feeding study):
- not examined
- Food efficiency:
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- not examined
- Clinical biochemistry findings:
- not examined
- Urinalysis findings:
- not examined
- Behaviour (functional findings):
- no effects observed
- Immunological findings:
- not examined
- Organ weight findings including organ / body weight ratios:
- not examined
- Histopathological findings: non-neoplastic:
- no effects observed
- Histopathological findings: neoplastic:
- no effects observed
- Other effects:
- not examined
- Reproductive function: oestrous cycle:
- not examined
- Reproductive function: sperm measures:
- not examined
- Reproductive performance:
- no effects observed
- Key result
- Dose descriptor:
- NOAEL
- Remarks:
- (systemic/fertility)
- Effect level:
- >= 2 000 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Remarks on result:
- other: (corresponding to 1.5%)
- Clinical signs:
- no effects observed
- Mortality / viability:
- no mortality observed
- Body weight and weight changes:
- no effects observed
- Food consumption and compound intake (if feeding study):
- not examined
- Food efficiency:
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- not examined
- Clinical biochemistry findings:
- not examined
- Urinalysis findings:
- not examined
- Sexual maturation:
- no effects observed
- Organ weight findings including organ / body weight ratios:
- not examined
- Gross pathological findings:
- not examined
- Histopathological findings:
- no effects observed
- Description (incidence and severity):
- A histological examination of selected tissues from the rats of the second generation which showed a reduction in the percentage of animals weaned failed to show any lesions which could be ascribed to the consumption of PGPR.
- Other effects:
- not examined
- Behaviour (functional findings):
- not examined
- Developmental immunotoxicity:
- not examined
- Key result
- Dose descriptor:
- NOAEL
- Remarks:
- (systemic/fertility)
- Generation:
- F1
- Effect level:
- >= 2 000 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Remarks on result:
- other: (corresponding to 1.5%)
- Clinical signs:
- no effects observed
- Mortality / viability:
- no mortality observed
- Body weight and weight changes:
- no effects observed
- Food consumption and compound intake (if feeding study):
- not examined
- Food efficiency:
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- not examined
- Clinical biochemistry findings:
- not examined
- Urinalysis findings:
- not examined
- Sexual maturation:
- no effects observed
- Organ weight findings including organ / body weight ratios:
- not examined
- Gross pathological findings:
- not examined
- Histopathological findings:
- not examined
- Other effects:
- not examined
- Behaviour (functional findings):
- not examined
- Developmental immunotoxicity:
- not examined
- Key result
- Dose descriptor:
- NOAEL
- Remarks:
- (systemic/fertility)
- Generation:
- F2
- Effect level:
- >= 2 000 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Remarks on result:
- other: (corresponding to 1.5%)
- Reproductive effects observed:
- no
Reference
There were no significant differences in clinical signs in treated or control rats which indicated a treatment-related effect of PGPR.
- SURVIVAL AND CLINICAL SIGNS:
There were no deaths during the experimental period and no evidence of abnormal behaviour or functional disorder associated with the consumption of PGPR.
- BREEDING PERFORMANCDE:
Breeding performance for both the control and PGPR groups appeared to be more successful in the first generation (P0) as in the second generation (F1). In generation 1 (P0) a high percentage of the offspring was weaned for both groups.
There were no significant differences in clinical signs in treated or control rats which indicated a treatment-related effect.
- SURVIVAL AND CLINICAL SIGNS:
There were no deaths during the experimental period and no evidence of abnormal behaviour or functional disorder associated with the consumption of PGPR.
- BREEDING PERFORMANCE:
In the second generation (F1), breeding performance was poor for both diets with the only signifcant difference being that control rats had a signifcantly greater percentage of litters weaned entirely, which was reversed to the PGPR rats in the third generation (F2). An increase in the number of females which failed to breed was evident in the second generation (F1) compared to the first generation (P0). However, as the number of females failing to breed is comparable between the treatment and control group, the decrease in breeding success is not considered as related to test substance intake. One further difference in the second generation (F1) was the higher proportion of males among the weaned rats fed PGPR. As rats were not sexed until weaning, it is not known if this is due to a higher proportion of males being born, or to the males surviving better than the females. In the second generation (F1) there was a reduction in the percentage of animals weaned. As this reduction occurred in both groups and to a similar extent it is concluded that this was due to an unknown environmental factor.
- HISTOPATHOLOGY:
A histological examination of selected tissues from the rats of the second generation (F1) which showed a reduction in the percentage of animals weaned continued for 1 year failed to show any lesions which could be ascribed to the consumption of PGPR.
There were no significant differences in clinical signs in treated or control rats which indicated a treatment-related effect of PGPR.
- SURVIVAL AND CLINICAL SIGNS:
There were no deaths during the experimental period and no evidence of abnormal behaviour or functional disorder associated with the consumption of PGPR.
- BREEDING PERFORMANCE:
Breeding performance for both the control and PGPR groups appeared to be more successful in the third generation (F2) as in the second generation (F1). In
generation 3 (F2) a high percentage of the offspring were weaned for both groups. An increase in the number of females which failed to breed was evident in the third generation (F2) compared to the first generation (P0). However, as the number of females failing to breed is comparable between the respective treatment and control group, the decrease in breeding success is not considered as related to test substance intake.
In conclusion, the similarity observed between the data obtained for the first (P0) and third generations (F2) failed to provide any evidence of a cumulative effect due to long-term ingestion of PGPR over three successive generations.
Effect on fertility: via oral route
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 2 000 mg/kg bw/day
- Quality of whole database:
- The available information comprises an adequate and reliable (RL2) key study with a read-across substance. The information is therefore sufficient to fulfil the standard information requirements set out in Annex VIII, 8.7, of Regulation (EC) No 1907/2006.
Effect on fertility: via inhalation route
- Endpoint conclusion:
- no study available
Effect on fertility: via dermal route
- Endpoint conclusion:
- no study available
Additional information
Toxicity to reproduction
Justification for read-across
There are no data regarding reproductive toxicity available for Polyaldo 2-1-IS (CAS 73296-86-3). In order to fulfil the standard data requirements defined in Regulation (EC) No 1907/2006, Annex VIII, 8.7, read-across from an appropriate substance is conducted in accordance with Regulation (EC) No 1907/2006, Annex XI, 1.5. Structural similarities and similarities in properties and/or activities of the source and target substance are the basis of read-across. A detailed justification for the analogue read-across approach is provided in the technical dossier (see IUCLID Section 13).
As no data is available regarding reproductive toxicity for Polyaldo 2-1-IS (CAS 73296-86-3) information from the analogue substance Polyglycerol polyrizinoleate (PGPR; CAS 29894-35-7) are taken into account to fulfill the standard data requirements defined in Regulation (EC) No 1907/2006, Annex VIII, 8.7.
CAS 29894-35-7
During a three-generation reproduction toxicity study (non-guideline, non-GLP) male and female Colworth Wistar rats were exposed to the test item at concentrations of 1.5% (w/w) in diet (Wilson and Smith, 1998). Breeding females consumed levels of greater than 2 g/kg bw/day based on increased food intake of up to 40 g/day during lactation. A continuous breeding protocol was adopted, in which the breeding pairs were maintained until the female had produced five litters or when it became evident that breeding had ceased. The main focus of the study design was to observe any effect on breeding. The parameters measured in each of the three generations (P0, F1, F2) included number of litters per dam, average litter size, average weaning weights of males and females, litters per group showing 100% survival and total survival (%) at day 21. Growth was normal throughout the three generations and there were no deaths or clinical signs associated with the consumption of the test substance in any litter. The only significant change in breeding performance was a reduction in the percentage of animals weaned in the second generation (F1), but as this occurred in the control group to a similar extent it was concluded that this was due to an unknown environmental factor and was not treatment related. A histological examination of selected tissues from those rats continued for 1 year failed to show any lesions which could be ascribed to the consumption of the test substance. An increase in the number of females which failed to breed was evident in the second (F1) and third generation (F2) compared to the first generation (P0). However, as the number of females failing to breed is comparable between the respective treatment and control group, the decrease in breeding success is not considered as related to test substance intake. In conclusion, rats fed 1.5% (w/w) of the test substance did not produce any adverse effect on reproductive capacity or development of the offspring during three generations of continuous exposure. As there was only one concentration tested without effects, a NOAEL ≥ 2000 m/kg w/day is derived.
Conclusion for reproduction toxicity
The available data show that the analogue substance Polyglycerol polyrizinoleate (PGPR; CAS 29894-35-7) does not possess intrinsic hazardous properties in regard to reproduction toxicity. Therefore, based on common functional groups and structural similarities, Polyaldo 2-1-IS (CAS 73296-86-3) is considered to be non-hazardous regarding reproduction toxicity.
Effects on developmental toxicity
Description of key information
- 3-generation reproduction study (non-guideline study, RL2), rats, diet: no effects observed
Effect on developmental toxicity: via oral route
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 2 000 mg/kg bw/day
- Quality of whole database:
- The available information comprises an adequate and reliable (RL2) key study with a read-across substance. The information is therefore sufficient to fulfil the standard information requirements set out in Annex VIII, 8.7, of Regulation (EC) No 1907/2006.
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
Developmental toxicity
Justification for read-across
There are no data regarding reproduction toxicity available for Polyaldo 2-1-IS (CAS 73296-86-3). In order to fulfil the standard data requirements defined in Regulation (EC) No 1907/2006, Annex VIII, 8.7, read-across from appropriate substances is conducted in accordance with Regulation (EC) No 1907/2006, Annex XI, 1.5. Structural similarities and similarities in properties and/or activities of the source and target substance are the basis of read-across. A detailed justification for the analogue read-across approach is provided in the technical dossier (see IUCLID Section 13).
As no data is available regarding developmental toxicity for Polyaldo 2-1-IS (CAS 73296-86-3) information from the analogue substance Polyglycerol polyrizinoleate (PGPR; CAS 29894-35-7) are taken into account to fulfill the standard data requirements defined in Regulation (EC) No 1907/2006, Annex VIII, 8.7.
CAS 29894-35-7
During a three-generation reproduction toxicity study (non-guideline, non-GLP) male and female Colworth Wistar rats were exposed to the test item at concentrations of 1.5% (w/w) in diet (Wilson and Smith, 1998). Breeding females consumed levels of greater than 2 g/kg bw/day based on increased food intake of up to 40 g/day during lactation. A continuous breeding protocol was adopted, in which the breeding pairs were maintained until the female had produced five litters or when it became evident that breeding had ceased. The main focus of the study design was to observe any effect on breeding. The parameters measured in each of the three generations included number of litters per dam, average litter size, average weaning weights of males and females, litters per group showing 100% survival and total survival (%) at day 21. Growth was normal throughout the three generations and there were no deaths or clinical signs associated with the consumption of the test substance. Rats fed 1.5% (w/w) of the test substance did not produce any adverse effect on reproductive capacity or development of the offspring during three generations of continuous exposure. As there was only one concentration tested without effects, a NOAEL ≥ 2000 m/kg w/day is derived.
Conclusion for developmental toxicity
The available data show that the analogue substance Polyglycerol polyrizinoleate (PGPR; CAS 29894-35-7) did not provide evidence to indicate that it negatively affects organogenesis or fetal development in utero. Thus, Polyaldo 2-1-IS (CAS 73296-86-3) is not expected to exhibit developmental toxicity/teratogenicity.
Justification for classification or non-classification
The available data on fertility with the appropriate read-across substance Polyglycerol polyrizinoleate (CAS 29894-35-7) do not meet the criteria for classification according to Regulation (EC) No 1272/2008, and are therefore conclusive but not sufficient for classification.
The available data on developmental toxicity with the appropriate read-across substance Polyglycerol polyrizinoleate (CAS 29894-35-7) do not meet the criteria for classification according to Regulation (EC) No 1272/2008, and are therefore conclusive but not sufficient for classification.
Additional information
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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