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EC number: 941-924-2 | 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
Short-term toxicity to fish
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to fish
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1995
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 203 (Fish, Acute Toxicity Test)
- Version / remarks:
- 1984
- Deviations:
- no
- GLP compliance:
- yes
- Analytical monitoring:
- yes
- Details on sampling:
- Samples for analysis were taken at 0, 24, 48, 72 and 96 hours old and new for all concentrations. A sample of the stock was also taken each day. Analysis indicated that mean measured concentrations were between 68 and 70 % of nominal over the duration of the test
- Vehicle:
- no
- Details on test solutions:
- At 0 hours 3.2 g of Priolube 3934 (Q038-03) was weighed out and dispersed in 5 Iitres of carbon filtered tap water by high-shear mixing at 20,000 rpm for 30
minutes in a 5 litre conical flask to maximize the shearing effect of the blade. This gave a 640 mg/I stock. This stock was prepared daily with the test solutions
prepared by appropriate dilution of the stock as outlined in Table 1 (see below) - Test organisms (species):
- Danio rerio (previous name: Brachydanio rerio)
- Details on test organisms:
- The fish used in this study were taken from batch 36Z which hatched on 17/3/95.
They were reared in carbon-filtered tap water and fed on proprietary fish food.
There were no significant mortalities of the test fish in the week prior to the test.
A fish survey was carried out at the end of the test. Fish from the control tank indicated a mean weight of 0.20 g and a mean length of 3.1 cm.
In a deviation from SOP 108 04 not all of the fish surveyed were 2.0 ± 1.0 cm in length. This is not considered to have affected the outcome of the study. - Test type:
- semi-static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 96 h
- Hardness:
- See table 2
- Test temperature:
- See table 2
- pH:
- See table 2
- Dissolved oxygen:
- See table 2
- Nominal and measured concentrations:
- See table 3
- Details on test conditions:
- The method was a static renewal procedure with test renewals every 24 hours. The test vessels were 6 litre capacity all-glass tanks containing 5 Iitres of test solution.
There were no replicates and all vessels were aerated. The fish were observed daily for any abnormalities in swimming activity and loss of balance. - Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- > 124 mg/L
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Details on results:
- There were no mortalities at any of the test concentrations. There were no visible abnormalities, and fish behaviour was unaffected at any of the test concentrations.
- Validity criteria fulfilled:
- yes
- Conclusions:
- Priolube 3934 is not acutely toxic to Zebra fish at a mean measured concentration of 124 mg/1. The 96 hour LC50 is greater than 124 mg/1. Observations of the fish
indicated that fish behaviour was not affected and there were no visible abnormalities at the tested concentrations. The 96 hour NOEC is > 124 mg/l.
LC50 (96h) >124 mg/L - Endpoint:
- short-term toxicity to fish
- Type of information:
- other: Read across on analogous substance
- Adequacy of study:
- supporting study
- Study period:
- 1995
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 203 (Fish, Acute Toxicity Test)
- Version / remarks:
- 1984
- Deviations:
- no
- GLP compliance:
- yes
- Analytical monitoring:
- yes
- Details on sampling:
- Samples for analysis were taken at 0, 24, 48, 72 and 96 hours old and new for all concentrations. A sample of the stock was also taken each day. Analysis indicated that mean measured concentrations were between 27 and 36 % of nominal over the duration of the test
- Vehicle:
- no
- Details on test solutions:
- At 0 hours 3.2 g of the substance was weighed out and dispersed in 5 litres of carbon filtered tap water by high-shear mixing at 15,000 rpm for 30
minutes in a 5 litre conical flask to maximize the shearing effect of the blade. This gave a 640 mg/I stock. This stock was prepared daily with the test solutions prepared by appropriate dilution of the stock as outlined in Table 1. (see below) - Test organisms (species):
- Danio rerio (previous name: Brachydanio rerio)
- Details on test organisms:
- The fish used in this study were taken from batch 36Z which hatched on 17/3/95.
They were reared in carbon-filtered tap water and fed on proprietary fish food.
There were no significant mortalities of the test fish in the week prior to the test.
A fish survey was carried out at the end of the test. Fish from the control tank indicated a mean weight of 0.20 g and a mean length of 3.1 cm.
In a deviation from SOP 108 04 not all of the fish surveyed were 2.0 ± 1.0 cm in length. This is not considered to have affected the outcome of the study. - Test type:
- semi-static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 96 h
- Hardness:
- See table 2
- Test temperature:
- See table 2
- pH:
- See table 2
- Dissolved oxygen:
- See table 2
- Nominal and measured concentrations:
- Nominal: 0, 18, 32, 56, 100 and 180 mg/L
Measured: 0, 6.5, 9.7, 16.1, 27.8 and 48.3 mg/L
See table 3 - Details on test conditions:
- The method was a static renewal procedure with test renewals every 24 hours. The test vessels were 6 litre capacity all-glass tanks containing 5 Iitres of test solution.
There were no replicates and all vessels were aerated. The fish were observed daily for any abnormalities in swimming activity and loss of balance.
TEST SYSTEM
- Test vessel:
- Material, size, fill volume: 6 L all-glass tanks containing 5 L of test solution
- Aeration: yes
- Renewal rate of test solution (frequency): every 24 hours
- No. of organisms per vessel: 7
- No. of vessels per concentration (replicates): 1
- No. of vessels per control (replicates): 1
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Carbon filtered tap water
- Intervals of water quality measurement: Daily for pH, dissolved oxygen, total hardness and temperature.
OTHER TEST CONDITIONS
- Photoperiod: 16 h light/ 8 h dark
EFFECT PARAMETERS MEASURED (with observation intervals if applicable): Mortalities and symptoms of toxicity were determined daily. The fish from the control were weighed and measured at the end of the exposure period - Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- > 48 mg/L
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Details on results:
- There were no mortalities at any of the test concentrations. There were no visible abnormalities, and fish behaviour was unaffected at any of the test concentrations.
- Validity criteria fulfilled:
- yes
- Conclusions:
- Priolube 3988 is not acutely toxic to Zebra fish at a mean measured concentration of 48 mg/l. The 96 hour LC50 is greater than 48 mg/l. Observations of the fish
indicated that fish behaviour was not affected and there were no visible abnormalities at the tested concentrations. The 96 hour NOEC is > 48 mg/l. - Endpoint:
- short-term toxicity to fish
- Type of information:
- (Q)SAR
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Justification for type of information:
- QSAR prediction: migrated from IUCLID 5.6
- Qualifier:
- no guideline required
- Principles of method if other than guideline:
- Ecosar v1.00, integrated in EpiSuite was used.
- GLP compliance:
- no
- Test organisms (species):
- other: fish
- Test type:
- other: (Q)SAR evaluation
- Water media type:
- freshwater
- Total exposure duration:
- 96 h
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- 0.008 mg/L
- Nominal / measured:
- estimated
- Conc. based on:
- other: QSAR
- Basis for effect:
- mortality (fish)
- Remarks on result:
- other: The QSAR model indicates that the chemical may not be soluble enough to measure this predicted effect.
- Details on results:
- The water solubility as described in section 4.8 of IUCLID is < 0.04 mg/L. The QSAR estimate for the water solubility predicts that the actual solublity will be far below that value. The predicted water solubility is, in fact, 5.289 e-5 mg/L.
The log Kow of the substance as described in section 4.7 of IUCLID is > 6 (RA from the analogue TMP Pelargonate). The QSAR estimate for the Log Kow predicts that the partition coefficient will be far above that value. The predicted Log Kow is 8.674.
Based on the comparison of the water solubility with the estimated LC50 for fish it is clear that the substance is most likely not soluble enough to result in this predicted QSAR effect. In addition the QSAR model indicates that if the log Kow is > 5, and the LC50 exceeds the water solubility by a factor 10, no effects at saturation are predicted.
This is the case for this substance. Therefore, the conclusion is that no acute toxicity is predicted for this substance. - Sublethal observations / clinical signs:
Chemical may not be soluble enough to measure this predicted effect.
- Conclusions:
- The water solubility as described in section 4.8 of IUCLID is < 0.04 mg/L. The QSAR estimate for the water solubility predicts that the actual solublity will be far below that value. The predicted water solubility is 5.289e-5.
The log Kow of the substance as described in section 4.7 of IUCLID is > 6 (RA from the analogue TMP Pelargonate) . The QSAR estimate for the Log Kow predicts that the partition coefficient will be far above that value. The predicted Log Kow is 8.674.
Based on the comparison of the water solubility with the estimated LC50 for fish it is clear that the substance is most likely not soluble enough to result in this predicted QSAR effect. In addition the QSAR model indicates that if the log Kow is > 5, and the LC50 exceeds the water solubility by a factor 10, no effects at saturation are predicted.
This is the case for this substance. Therefore, the conclusion is that no acute toxicity is predicted for this substance. - Endpoint:
- short-term toxicity to fish
- Type of information:
- (Q)SAR
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Justification for type of information:
- QSAR prediction: migrated from IUCLID 5.6
- Qualifier:
- no guideline required
- Principles of method if other than guideline:
- Ecosar v1.00, integrated in EpiSuite was used.
- GLP compliance:
- no
- Test organisms (species):
- other: fish
- Test type:
- other: (Q)SAR evaluation
- Water media type:
- freshwater
- Total exposure duration:
- 96 h
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- 0.004 mg/L
- Nominal / measured:
- estimated
- Conc. based on:
- other: QSAR
- Basis for effect:
- mortality (fish)
- Remarks on result:
- other: The QSAR model indicates that the chemical may not be soluble enough to measure this predicted effect.
- Details on results:
- The water solubility as described in section 4.8 of IUCLID is < 0.04 mg/L. The QSAR estimate for the water solubility predicts that the actual solublity will be far below that value. The predicted water solubility is, in fact, 1.641 e-5 mg/L.
The log Kow of the substance as described in section 4.7 of IUCLID is > 6 (RA from the analogue TMP Pelargonate). The QSAR estimate for the Log Kow predicts that the partition coefficient will be far above that value. The predicted Log Kow is 9.165.
Based on the comparison of the water solubility with the estimated LC50 for fish it is clear that the substance is most likely not soluble enough to result in this predicted QSAR effect. In addition the QSAR model indicates that if the log Kow is > 5, and the LC50 exceeds the water solubility by a factor 10, no effects at saturation are predicted.
This is the case for this substance. Therefore, the conclusion is that no acute toxicity is predicted for this substance. - Sublethal observations / clinical signs:
Chemical may not be soluble enough to measure this predicted effect.
- Conclusions:
- The water solubility as described in section 4.8 of IUCLID is < 0.04 mg/L. The QSAR estimate for the water solubility predicts that the actual solublity will be far below that value. The predicted water solubility is 1.641 e-5.
The log Kow of the substance as described in section 4.7 of IUCLID is > 6 (RA from the analogue TMP Pelargonate) . The QSAR estimate for the Log Kow predicts that the partition coefficient will be far above that value. The predicted Log Kow is 9.165.
Based on the comparison of the water solubility with the estimated LC50 for fish it is clear that the substance is most likely not soluble enough to result in this predicted QSAR effect. In addition the QSAR model indicates that if the log Kow is > 5, and the LC50 exceeds the water solubility by a factor 10, no effects at saturation are predicted.
This is the case for this substance. Therefore, the conclusion is that no acute toxicity is predicted for this substance. - Endpoint:
- short-term toxicity to fish
- Type of information:
- (Q)SAR
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Justification for type of information:
- QSAR prediction: migrated from IUCLID 5.6
- Qualifier:
- no guideline required
- Principles of method if other than guideline:
- Ecosar v1.00, integrated in EpiSuite was used.
- GLP compliance:
- no
- Test organisms (species):
- other: fish
- Test type:
- other: (Q)SAR evaluation
- Water media type:
- freshwater
- Total exposure duration:
- 96 h
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- 0.002 mg/L
- Nominal / measured:
- estimated
- Conc. based on:
- other: QSAR
- Basis for effect:
- mortality (fish)
- Remarks on result:
- other: The QSAR model indicates that the chemical may not be soluble enough to measure this predicted effect.
- Details on results:
- The water solubility as described in section 4.8 of IUCLID is < 0.04 mg/L. The QSAR estimate for the water solubility predicts that the actual solublity will be far below that value. The predicted water solubility is, in fact, 5.084 e-6 mg/L.
The log Kow of the substance as described in section 4.7 of IUCLID is > 6 (RA from the analogue TMP Pelargonate). The QSAR estimate for the Log Kow predicts that the partition coefficient will be far above that value. The predicted Log Kow is 9.656.
Based on the comparison of the water solubility with the estimated LC50 for fish it is clear that the substance is most likely not soluble enough to result in this predicted QSAR effect. In addition the QSAR model indicates that if the log Kow is > 5, and the LC50 exceeds the water solubility by a factor 10, no effects at saturation are predicted.
This is the case for this substance. Therefore, the conclusion is that no acute toxicity is predicted for this substance. - Sublethal observations / clinical signs:
Chemical may not be soluble enough to measure this predicted effect.
- Conclusions:
- The water solubility as described in section 4.8 of IUCLID is < 0.04 mg/L. The QSAR estimate for the water solubility predicts that the actual solublity will be far below that value. The predicted water solubility is, in fact, 5.084 e-6 mg/L.
The log Kow of the substance as described in section 4.7 of IUCLID is > 6 (RA from the analogue TMP Pelargonate). The QSAR estimate for the Log Kow predicts that the partition coefficient will be far above that value. The predicted Log Kow is 9.656.
Based on the comparison of the water solubility with the estimated LC50 for fish it is clear that the substance is most likely not soluble enough to result in this predicted QSAR effect. In addition the QSAR model indicates that if the log Kow is > 5, and the LC50 exceeds the water solubility by a factor 10, no effects at saturation are predicted.
This is the case for this substance. Therefore, the conclusion is that no acute toxicity is predicted for this substance. - Endpoint:
- short-term toxicity to fish
- Type of information:
- (Q)SAR
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Justification for type of information:
- QSAR prediction: migrated from IUCLID 5.6
- Qualifier:
- no guideline required
- Principles of method if other than guideline:
- Ecosar v1.00, integrated in EpiSuite was used.
- GLP compliance:
- no
- Test organisms (species):
- other: fish
- Test type:
- other: (Q)SAR evaluation
- Water media type:
- freshwater
- Total exposure duration:
- 96 h
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- 0.001 mg/L
- Nominal / measured:
- estimated
- Conc. based on:
- other: QSAR
- Basis for effect:
- mortality (fish)
- Remarks on result:
- other: The QSAR model indicates that the chemical may not be soluble enough to measure this predicted effect.
- Details on results:
- The water solubility as described in section 4.8 of IUCLID is < 0.04 mg/L. The QSAR estimate for the water solubility predicts that the actual solublity will be far below that value. The predicted water solubility is, in fact, 1.574 e-6 mg/L.
The log Kow of the substance as described in section 4.7 of IUCLID is > 6 (RA from the analogue TMP Pelargonate). The QSAR estimate for the Log Kow predicts that the partition coefficient will be far above that value. The predicted Log Kow is 10.147.
Based on the comparison of the water solubility with the estimated LC50 for fish it is clear that the substance is most likely not soluble enough to result in this predicted QSAR effect. In addition the QSAR model indicates that if the log Kow is > 5, and the LC50 exceeds the water solubility by a factor 10, no effects at saturation are predicted.
This is the case for this substance. Therefore, the conclusion is that no acute toxicity is predicted for this substance. - Sublethal observations / clinical signs:
Chemical may not be soluble enough to measure this predicted effect.
- Conclusions:
- The water solubility as described in section 4.8 of IUCLID is < 0.04 mg/L. The QSAR estimate for the water solubility predicts that the actual solublity will be far below that value. The predicted water solubility is, in fact, 1.574 e-6 mg/L.
The log Kow of the substance as described in section 4.7 of IUCLID is > 6 (RA from the analogue TMP Pelargonate). The QSAR estimate for the Log Kow predicts that the partition coefficient will be far above that value. The predicted Log Kow is 10.147.
Based on the comparison of the water solubility with the estimated LC50 for fish it is clear that the substance is most likely not soluble enough to result in this predicted QSAR effect. In addition the QSAR model indicates that if the log Kow is > 5, and the LC50 exceeds the water solubility by a factor 10, no effects at saturation are predicted.
This is the case for this substance. Therefore, the conclusion is that no acute toxicity is predicted for this substance. - Endpoint:
- short-term toxicity to fish
- Type of information:
- (Q)SAR
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Justification for type of information:
- QSAR prediction: migrated from IUCLID 5.6
- Qualifier:
- no guideline required
- Principles of method if other than guideline:
- Ecosar v1.00, integrated in EpiSuite was used.
- GLP compliance:
- no
- Test organisms (species):
- other: fish
- Test type:
- other: (Q)SAR evaluation
- Water media type:
- freshwater
- Total exposure duration:
- 96 h
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- 0.001 mg/L
- Nominal / measured:
- estimated
- Conc. based on:
- other: QSAR
- Basis for effect:
- mortality (fish)
- Remarks on result:
- other: The QSAR model indicates that the chemical may not be soluble enough to measure this predicted effect.
- Details on results:
- The water solubility as described in section 4.8 of IUCLID is < 0.04 mg/L. The QSAR estimate for the water solubility predicts that the actual solublity will be far below that value. The predicted water solubility is, in fact, 4.871 e-7 mg/L.
The log Kow of the substance as described in section 4.7 of IUCLID is > 6 (RA from the analogue TMP Pelargonate). The QSAR estimate for the Log Kow predicts that the partition coefficient will be far above that value. The predicted Log Kow is 10.639.
Based on the comparison of the water solubility with the estimated LC50 for fish it is clear that the substance is most likely not soluble enough to result in this predicted QSAR effect. In addition the QSAR model indicates that if the log Kow is > 5, and the LC50 exceeds the water solubility by a factor 10, no effects at saturation are predicted.
This is the case for this substance. Therefore, the conclusion is that no acute toxicity is predicted for this substance. - Sublethal observations / clinical signs:
Chemical may not be soluble enough to measure this predicted effect.
- Conclusions:
- The water solubility as described in section 4.8 of IUCLID is < 0.04 mg/L. The QSAR estimate for the water solubility predicts that the actual solublity will be far below that value. The predicted water solubility is, in fact, 4.871 e-7 mg/L.
The log Kow of the substance as described in section 4.7 of IUCLID is > 6 (RA from the analogue TMP Pelargonate). The QSAR estimate for the Log Kow predicts that the partition coefficient will be far above that value. The predicted Log Kow is 10.639.
Based on the comparison of the water solubility with the estimated LC50 for fish it is clear that the substance is most likely not soluble enough to result in this predicted QSAR effect. In addition the QSAR model indicates that if the log Kow is > 5, and the LC50 exceeds the water solubility by a factor 10, no effects at saturation are predicted.
This is the case for this substance. Therefore, the conclusion is that no acute toxicity is predicted for this substance. - Endpoint:
- short-term toxicity to fish
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Justification for type of information:
- The read across justification is reported at section 13
- Reason / purpose for cross-reference:
- read-across source
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- > 124 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Validity criteria fulfilled:
- yes
- Conclusions:
- Priolube 3934 is not acutely toxic to Zebra fish at a mean measured concentration of 124 mg/1. The 96 hour LC50 is greater than 124 mg/1. Observations of the fish
indicated that fish behaviour was not affected and there were no visible abnormalities at the tested concentrations. The 96 hour NOEC is > 124 mg/l.
LC50 (96h) >124 mg/L
Referenceopen allclose all
Description of key information
Two studies have been conducted (one on the target substance TMP Pelargonate and one on the analogue TMP Triisostearate) indicating no effect at the maximum tested concentration, equivalent to nominal 180 mg/l. The measured concentrations are much lower due to the water solubility and hydrolytic instability of the substances.
Because no hazard was identified, no key values for chemical safety assessment are given below.
LC0 of TMP tripelargonate > 124 mg/l
LC0 of TMP isotristearate > 48 mg/l
Qsar generated data are also available on short term toxicity for the constituents of this UVCB substance.
Key value for chemical safety assessment
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.