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Diss Factsheets
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EC number: 251-178-3 | CAS number: 32724-62-2
- 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
Long-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
- Endpoint:
- long-term toxicity to aquatic invertebrates
- Type of information:
- (Q)SAR
- Adequacy of study:
- key study
- Study period:
- 30 March 2022 to 05 April 2022
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- results derived from a valid (Q)SAR model, but not (completely) falling into its applicability domain, with adequate and reliable documentation / justification
- Remarks:
- The test item falls within the applicability domain of the model except for the descriptor domain. Therefore, the predicted CHRONIC TOXICITY TO DAPHNIDS (21-DAY EC10) is considered as an extrapolation. This result can be considered as reliable with restrictions (descriptor domain).
- Justification for type of information:
- 1. SOFTWARE
iSafeRat® – in Silico Algorithms For Environmental Risk And Toxicity
2. MODEL (incl. version number)
iSafeRat® daphEC10 v1.5
3. SMILES OR OTHER IDENTIFIERS USED AS INPUT FOR THE MODEL
CCc1cc(C)cc(CC)c1Nc2ccc(Nc3c(CC)cc(C)cc3CC)c4C(=O)c5ccccc5C(=O)c24
4. SCIENTIFIC VALIDITY OF THE (Q)SAR MODEL
See attached QMRF
5. APPLICABILITY DOMAIN
See attached Study Report with QPRF in Annex
6. ADEQUACY OF THE RESULT
See attached Study Report with QPRF in Annex - Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 211 (Daphnia magna Reproduction Test)
- Deviations:
- not applicable
- Remarks:
- QSAR model
- Principles of method if other than guideline:
- The CHRONIC TOXICITY TO DAPHNIDS (21-DAY EC10) was determined using iSafeRat® daphEC10, a validated QSAR model for the Mechanism of Action (MechoA) in question (MechoA 1.1, i.e. non-polar narcosis) (Bauer et al., 2018). The QSAR is based on validated data for a training set of 31 chemicals derived from 21-day test on daphnids, for which the concentrations of the test item had been determined by chemical analyses over the test period.
- GLP compliance:
- no
- Remarks:
- QSAR model
- Analytical monitoring:
- no
- Remarks:
- QSAR model
- Details on sampling:
- not applicable
- Vehicle:
- no
- Details on test solutions:
- not applicable
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- none
- Test type:
- other: QSAR model
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 21 d
- Remarks on exposure duration:
- Results from a test duration of 21 days only were used for Daphnia magna.
- Post exposure observation period:
- not applicable
- Hardness:
- The QSAR is based on data from studies performed at acceptable hardness to ensure control survival.
- Test temperature:
- The temperatures varied from approximately 20 to 23 °C. This small difference is not expected to contribute to the variability of the values found in experimental data.
- pH:
- Test results were taken from studies with measured pHs between 6 - 9.
- Dissolved oxygen:
- The model is based on data from studies performed at acceptable oxygen concentrations (generally >60%).
- Salinity:
- not applicable
- Conductivity:
- not applicable
- Nominal and measured concentrations:
- Studies were used only where sufficient evidence was presented to determine that the stubstance was stable under test conditions (i.e. maintened within ± 20 % of the nominal) or, if not, the result was based on measured concentrations as geometric mean.
- Details on test conditions:
- Preferentially results from a flow-through studies were used. However semi-static with daily renewal of test solutions and the control was accepted (preferably accompanied by analytical measurements over the study period). For suspected volatile substances only tests performed in closed vessels were accepted unless accompanying analytical monitoring proved such a design was not necessary.
- Reference substance (positive control):
- not required
- Key result
- Duration:
- 21 d
- Dose descriptor:
- EC10
- Remarks:
- equivalent to MATC
- Effect conc.:
- > 0.003 mg/L
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- test mat.
- Basis for effect:
- reproduction
- Details on results:
- The test item falls within the applicability domain of the model except for the descriptor domain. Therefore, the predicted CHRONIC TOXICITY TO DAPHNIDS (21-DAY EC10) is considered as an extrapolation. This result can be considered as reliable with restrictions (descriptor domain).
- Results with reference substance (positive control):
- not applicable
- Reported statistics and error estimates:
- 95% confidence interval (α = 0.05): not applicable
- Alcohol
- Alkane
- Alkene
- Anthraquinones
- Aromatic hydrocarbons and polycyclic aromatic hydrocarbon
- Ester
- Ether
- Halogenated hydrocarbons
- Ketone
- non-polar narcosis (MechoA 1.1)
- mono-/poly-esters whose hydrolysis products are narcotics (MechoA 2.1)
- Validity criteria fulfilled:
- yes
- Conclusions:
- The test item falls within the applicability domain of the model except for the descriptor domain. Therefore, the predicted CHRONIC TOXICITY TO DAPHNIDS (21-DAY EC10) is considered as an extrapolation. This result can be considered as reliable with restrictions (descriptor domain).
The CHRONIC TOXICITY TO DAPHNIDS (21-DAY EC10) of the test item was predicted as greater than the water solubility value within the exposure period of the test.
95% confidence interval (α = 0.05): not applicable - Executive summary:
A Quantitative Structure Activity Relationship (QSAR) model was used to calculate the CHRONIC TOXICITY TO DAPHNIDS (21-DAY EC10) for the test item. This QSAR model has been validated to be compliant with the OECD recommendations for QSAR modeling (OECD, 2004) and predicts the endpoint value which would be expected when testing the substance under experimental conditions in a laboratory following Guideline for Testing of Chemicals No. 211, "Daphnia magna Reproduction Test" (OECD, 2012). The criterion predicted was the EC10 (10% Effective Concentration), a concentration which is expected to cause an effect of 10% on reproducibility within a period of 21 days.
The CHRONIC TOXICITY TO DAPHNIDS (21-DAY EC10) was determined using iSafeRat® daphEC10, a validated QSAR model for the Mechanism of Action (MechoA) in question (MechoA 1.1, i.e. non-polar narcosis) (Bauer et al., 2018). The QSAR is based on validated data for a training set of 31 chemicals derived from 21-day test on daphnids, for which the concentrations of the test item had been determined by chemical analyses over the test period.
The test item falls within the applicability domain of the model except for the descriptor domain. Therefore, the predicted CHRONIC TOXICITY TO DAPHNIDS (21-DAY EC10) is considered as an extrapolation. This result can be considered as reliable with restrictions (descriptor domain).
The CHRONIC TOXICITY TO DAPHNIDS (21-DAY EC10) of the test item was predicted as greater than the water solubility value within the exposure period of the test.
95% confidence interval (α = 0.05): not applicable
Reference
Descriptor domain
The Subcooled Liquid Water Solubility value (< -6.594 in log10 (mol/L)) given as the input to the iSafeRat® daphEC10 model does not fall within the descriptor domain of the model between -5.910 and 1.030 in log10 (mol/L). Therefore, the prediction is considered as an extrapolation.
Structural fragment domain
The variability of structure in the training set is not considered as a relevant domain since the model is based on a mechanistic approach (mechanism of action). Since the MechoA is related to the molecular structure, the following list of chemical moieties can give an overview of the structural domain:
The test item as an anthraquinone can be taken into account by the model.
Mechanistic domain:
The iSafeRat® daphEC10 model can reliably predict the aquatic toxicity for chemicals with the following mechanisms of action of toxicity (MechoA):
The MechoA of molecules is predicted directly from the structure. The test item as an aminoanthraquinone is expected to exert a MechoA 1.1 & m4.3: Non-polar narcosis for all species & metabolisation into nitroso generating protein and DNA adducts, oxidative stress, DNA adducts, cancer development for mammals only (Bauer et al., 2018). Therefore, the test item can be taken into account by the model in order to predict toxicity to non-mammal aquatic organisms.
Description of key information
21d-EC10 (Daphnia magna) > solubility limit; iSafeRat® High-Accuracy-Quantitative Structure-Activity Relationship; KREATiS (2022).
Key value for chemical safety assessment
Additional information
To strengthen the reliability of the HA-QSAR prediction and the category approach, one experimental chronic daphnia study is available on the source substance, Solvent Blue 104 (CAS No 116-75-6). In addition, a testing proposal for a chronic daphnia study is requested on the source substance, Solvent Green 28 (CAS No 4851-50-7). Both substances are members of the category. See the category approach justification document, attached in section 13, for further details.
Global overview of the category approach for the endpoint:
| Solvent Violet 36 | Solvent Green 3 | Reinblau RLW | Reinblau BLW | Solvent Blue 104# | Solvent Green 28 | |
Long-term toxicity to aquatic invertebrates | 21d-EC10 (D.magna) > solubility limit* | 21d-EC10 (D.magna) > solubility limit* | 21d-EC10 (D.magna) > solubility limit* | 21d-EC10 (D.magna) > solubility limit* | 21d-NOEC (D.magna) ³ 1.0 mg/L (nominal)$
21d-EC10 (D.magna) > solubility limit* | Testing proposal (OECD TG 211) |
# not registered by LANXESS, data with letter of access
* iSafeRat® High Accuracy QSAR predictions (KREATiS, 2022)
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