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EC number: 239-147-2 | CAS number: 15096-41-0
- 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:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- weight of evidence
- Justification for type of information:
- REPORTING FORMAT FOR THE ANALOGUE APPROACH
1. HYPOTHESIS FOR THE ANALOGUE APPROACH
In aqueous media, the target substance complexation reaction products of Tetrachloro-μ-hydroxy(μ-methacrylato-O:O')dichromium, isopropylalcohol and water (CAS 15096-41-0) dissociates into the three compounds methacrylic acid (CAS 79-41-4), chromium trichloride (CAS 10025-73-7) and propan-2-ol (CAS 67-63-0). Hence, methacrylic acid, chromium trichloride and propan-2-ol will be present regardless whether the target substance itself or methacrylic acid, chromium trichloride and propan-2-ol, respectively, were used as test material. Moreover, dissociation of the target substance (CAS 15096-41-0) is to be expected in aquatic environmental systems, which allows the read across between the target substance (CAS 15096-41-0) and the source substance chromium trichloride (CAS 10025-73-7).
2. SOURCE AND TARGET CHEMICAL(S) (INCLUDING INFORMATION ON PURITY AND IMPURITIES)
The purity of the source substance which was used in the most reliable test with fish (reference 6.1.1-3) is unknown. The target substance complexation reaction products of Tetrachloro-μ-hydroxy(μ-methacrylato-O:O')dichromium, isopropylalcohol and water (CAS 15096-41-0), has a purity of 100 % (w/w).
3. ANALOGUE APPROACH JUSTIFICATION
Experimental data i.e. acute toxicity studies with fish were available for source substance. The source substance was tested in an study similar to OECD Guideline 203. This study revealed an 96-h LC50 of 11.2 mg/L (nominal) . The information given on chromium trichloride (CAS 10025-73-7) is considered to be sufficient to cover the required endpoint information for the target substance complexation reaction products of Tetrachloro-μ-hydroxy(μ-methacrylato-O:O')dichromium, isopropylalcohol and water (CAS 15096-41-0). - Reason / purpose for cross-reference:
- read-across source
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- 11.2 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- element
- Remarks:
- chromium
- Basis for effect:
- mortality (fish)
- Endpoint:
- short-term toxicity to fish
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- weight of evidence
- Justification for type of information:
- REPORTING FORMAT FOR THE ANALOGUE APPROACH
1. HYPOTHESIS FOR THE ANALOGUE APPROACH
In aqueous media, the target substance complexation reaction products of Tetrachloro-μ-hydroxy(μ-methacrylato-O:O')dichromium, isopropylalcohol and water (CAS 15096-41-0) dissociates into the three compounds methacrylic acid (CAS 79-41-4), chromium trichloride (CAS 10025-73-7) and propan-2-ol (CAS 67-63-0). Hence, methacrylic acid, chromium trichloride and propan-2-ol will be present regardless whether the target substance itself or methacrylic acid, chromium trichloride and propan-2-ol, respectively, were used as test material. Moreover, dissociation of the target substance (CAS 15096-41-0) is to be expected in aquatic environmental systems, which allows the read across between the target substance (CAS 15096-41-0) and the source substance propan-2-ol (CAS 67-63-0).
2. SOURCE AND TARGET CHEMICAL(S) (INCLUDING INFORMATION ON PURITY AND IMPURITIES)
The purity of the source substance which was used in the most reliable test with fish (reference 6.1.1-5) is unknown. The target substance complexation reaction products of Tetrachloro-μ-hydroxy(μ-methacrylato-O:O')dichromium, isopropylalcohol and water (CAS 15096-41-0), has a purity of 100 % (w/w).
3. ANALOGUE APPROACH JUSTIFICATION
Experimental data i.e. acute toxicity studies with fish were available for source substance propan-2-ol (CAS 67-63-0). The source substance was tested in an study similar to OECD to Guideline 203. This study revealed an 96-h LC50 of 10000 mg/L (measured, not specified). The information given on propan-2-ol is considered to be sufficient to cover the required endpoint information for the target substance complexation reaction products of Tetrachloro-μ-hydroxy(μ-methacrylato-O:O')dichromium, isopropylalcohol and water (CAS 15096-41-0). - Reason / purpose for cross-reference:
- read-across source
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- 10 000 mg/L
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- 9 640 mg/L
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- 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:
- REPORTING FORMAT FOR THE ANALOGUE APPROACH
1. HYPOTHESIS FOR THE ANALOGUE APPROACH
In aqueous media, the target substance complexation reaction products of Tetrachloro-μ-hydroxy(μ-methacrylato-O:O')dichromium, isopropylalcohol and water (CAS 15096-41-0) dissociates into the three compounds methacrylic acid (CAS 79-41-4), chromium trichloride (CAS 10025-73-7) and propan-2-ol (CAS 67-63-0). Hence, methacrylic acid, chromium trichloride and propan-2-ol will be present regardless whether the target substance itself or methacrylic acid, chromium trichloride and propan-2-ol, respectively, were used as test material. Moreover, dissociation of the target substance (CAS 15096-41-0) is to be expected in aquatic environmental systems, which allows the read across between the target substance (CAS 15096-41-0) and the source substance methacrylic acid (CAS 79-41-4).
2. SOURCE AND TARGET CHEMICAL(S) (INCLUDING INFORMATION ON PURITY AND IMPURITIES)
The source substance which was used in the most reliable test with fish (reference 6.1.1-1), had a analytical purity of 99.72 %. The target substance, Tetrachloro-μ-hydroxy(μ-methacrylato-O:O')dichromium, isopropylalcohol and water (CAS 15096-41-0), has a purity of 100 % (w/w). Thus, the purity of the test materials is comparable.
3. ANALOGUE APPROACH JUSTIFICATION
Experimental data i.e. acute toxicity studies with fish were available for methacrylic acid. The source substance was tested in an study according to Guideline US EPA OTS 797.1400. This study revealed an effect level of LC50 = 85 mg/L (measured, not specified). The information given on source substance is considered to be sufficient to cover the required endpoint information for the target substance complexation reaction products of Tetrachloro-μ-hydroxy(μ-methacrylato-O:O')dichromium, isopropylalcohol and water (CAS 15096-41-0). - Reason / purpose for cross-reference:
- read-across source
- Key result
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- 833 mg/L
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
Referenceopen allclose all
Description of key information
In an acute toxicity test similar to OECD Guideline 203 with chromium trichloride (CAS 79-41-4), the 96-h LC50 was determined to be 11.2 mg/L (nominal). This value has been chosen in a worst case approach out of available data for the structural analogues Methacrylic acid (CAS 79-41-4), Chromium trichloride (CAS 10025-73-7) and Propan-2-ol (CAS 67-63-0).
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Effect concentration:
- 11.2 mg/L
Additional information
No data on toxicity to fish was availbale for the substance itself. In aqueous media, the substance dissociates into the three compounds methacrylic acid (CAS 79-41-4), chromium trichloride (CAS 10025-73-7) and propan-2-ol (CAS 67-63-0). Thus, dissociation of the target substance (CAS 15096 -41 -0) is to be expected in aquatic environmental systems. Therefore, a read across between the target substance (CAS 15096-41-0) and the source substances methacrylate (CAS 79-41-4), chromium trichloride (CAS 10025-73-7) and propan-2-ol (CAS 67-63-0) was conducted. The available studies were assesseed in a weight of evidence approach.
Data were available of a valid acute toxicity test with the structural analogue methacrylate (CAS 79-41-4) according to the guideline US EPA OTS 797.1400, twenty fish (Oncorhynchus mykiss) per concentration plus a dilution water control were used in a flow-through system with a duplicate nominal dosing regimen of 6.5, 13, 25, 50 and 100 mg/L. Fish were temperature acclimated in the absence of food for 72 hours before initiation of the test. Test temperature, dissolved oxygen and pH was measured at all test concentrations at 0, 48 and 96 hours. Samples for analytical measurements of the test item concentration were taken at 0 and 96 hrs. The measured test item concentrations were: 6.2, 12, 23, 46, and 97 mg/L. During the test, the hardness of the test media was 47 - 48 mg CaCO3/l, the temperature between 11 and 12 °C, the pH between 5.3 and 7.8 and the dissolved oxygen concentration in the range of 8.2 - 9.4 mg/L. In result, the 96-h NOEC and EC50 of the test item was determined to be 12 and 85 mg/L (based on measured concentrations), respectively. This value was chosen as key parameter for the risk assessment.
In a valid acute toxicity test with Scophthalmus maximus according to the OSPAR Protocols on Methods for the Testing of Chemicals Used in the Offshore Oil Industry, 1995, in a semi-static test system was investigated. Test temperature, dissolved oxygen and pH were measured at all test concentrations at 0, 48 and 96 hours. Samples for analytical measurements of the test item concentration were taken at 0 and 96 hrs. During the test, the temperature between 13 and 17 °C, the pH 8 were maintained. In result, the 96-h EC50 of the test item was determined to be 833 mg/L (based on measured concentrations), respectively. (reference 6.1.1-1).
In a study similar to OECD Guideline 203, the effects of pre-treatment of rainbow trouts by different concentrations of polychorinated biphenyls on the acute toxicity to six different contaminants (mercury(II), chromium(III), cyanides, nitrates, nitirite, and chlorides) was investigated. Acute toxicity to these contaminants was tested using a control group of rainbow trouts (no pre-treatment towards PCBs) a low level group (PCB concentration of 0.46 µg/g tissue) and a high level group (PCB concentration of 3.40 µg/g tissue). The results found for the control groups exposed to chromium(III) was a LC50 (96h) of 11.2 mg Cr/L. Results with animals from the low level and high level group were 9.0 and 7.05 mg Cr/L respectively. The result for the control group is considered representative for acute toxicity towards the structural analogue chromium trichloride (CAS 10025-73-7) and can be converted to LC50 (96h) of 57.4 mg/L as chromium trichloride hexahydrate (reference 6.1.1-3).
In an acute toxicity test with the structural analogue propan-2-ol (CAS 67-63-0) similar to OECD Guideline 203 with 4 fish (Pimephales promelas) per concentration of the test item (concentration levels not reported, 2 vessels per concentration, 2 animals per vessel) were exposed in a flow-through system over a period of 96.0 h. Additionally, a negative control (2 replicates) was performed. For the test solutions Lake Superior water was was used as dilution water. Its alkalinity was determined to be 42.2 mg/L Calcium Carbonate. The test temperature was 25 ± 1°C, the pH = 7.5 and the dissolved oxygen concentration greater than 60% of saturation. Mortality was recorded in two test runs after 1, 3, 6, 12, 24, 48, 72, and 96 hours. In result, the 96-h LC50 for the first test was determined to be 10000 mg/L, for the second test 9640 mg/L (reference 6.1.1 5).
Conclusion
Based on a worst case approach, the 96-h LC50 for the target substance is considered to be 11.2 mg/L as determined for chromium(III) (reference 6.1.1-3).
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