Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 248-654-8 | CAS number: 27776-01-8
- 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
Bioaccumulation: aquatic / sediment
Administrative data
Link to relevant study record(s)
- Endpoint:
- bioaccumulation in aquatic species: fish
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- results derived from a valid (Q)SAR model and falling into its applicability domain, with adequate and reliable documentation / justification
- Justification for type of information:
- Based on the results of the aerobic mineralisation study OECD 309 with two relevant constituents of Dibenzyltoluene (CAS 53585-53-8): o,m DBT and o,o DTPM, and one relevant impurity (tested in the OECD 309 study), the BCF calculations of these three compounds were refined using the US EPA EPISUITE software, which is considered a QSAR model prediction tool of particular relevance and interest in accordance with the ECHA Guidance on Information Requirements and Chemical Safety Assessment, Chapter R.11 (PBT/vPvB assessment).
- Principles of method if other than guideline:
- B assessments were conducted for each relevant compounds using the US EPA EPISUITE software KOWWIN v.1.68 and BCFBAF v3.01.
- GLP compliance:
- not specified
- Key result
- Type:
- BCF
- Value:
- 2 169 L/kg
- Calculation basis:
- other: regression based
- Remarks on result:
- other: relevant impurity
- Key result
- Type:
- BCF
- Value:
- 8 513 L/kg
- Calculation basis:
- other: regression based
- Remarks on result:
- other: o,o-DPTM
- Key result
- Type:
- BCF
- Value:
- 10 280 L/kg
- Calculation basis:
- other: regression based
- Remarks on result:
- other: o,m-DBT
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The estimated BCF value is 10 280 L/kg wet-wt for the compound o,m-DBT, meaning that this compound is potentially very bioaccumulable.
The estimated BCF value is 8513 L/kg wet-wt for the compound o,o-DTPM, meaning that this compound is potentially very bioaccumulable.
The estimated BCF value is 2169 L/kg wet-wt for the relevant impurity of DBT substance, meaning that this compound is potentially bioaccumulable. - Executive summary:
Summary Results for the relevant impurity:
Log BCF (regression-based estimate): 3.34 (BCF = 2.17e+003 L/kg wet-wt)
Biotransformation Half-Life (days) : 6.34 (normalized to 10 g fish)
Log BAF (Arnot-Gobas upper trophic): 3.29 (BAF = 1.95e+003 L/kg wet-wt)Summary Results for o,o-DTPM:
Log BCF (regression-based estimate): 3.93 (BCF = 8.51e+003 L/kg wet-wt)
Biotransformation Half-Life (days) : 16.7 (normalized to 10 g fish)
Log BAF (Arnot-Gobas upper trophic): 4.94 (BAF = 8.65e+004 L/kg wet-wt)Summary Results for o,m-DBT:
Log BCF (regression-based estimate): 4.01 (BCF = 1.03e+004 L/kg wet-wt)
Biotransformation Half-Life (days) : 3.43 (normalized to 10 g fish)
Log BAF (Arnot-Gobas upper trophic): 5.67 (BAF = 4.66e+005 L/kg wet-wt)- Endpoint:
- bioaccumulation in aquatic species: fish
- Type of information:
- (Q)SAR
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- results derived from a valid (Q)SAR model and falling into its applicability domain, with adequate and reliable documentation / justification
- Justification for type of information:
- QSAR prediction
- Principles of method if other than guideline:
- calculation of BCF from experimental log Kow = 6.38, according to accepted model.
- Key result
- Type:
- BCF
- Value:
- 7 525 L/kg
- Calculation basis:
- other: regression based
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The estimated BCF is 7525 L/kg wet-wt, meaning that the substance is potentially bioaccumulable.
- Executive summary:
Summary Results:
Log BCF (regression-based estimate): 3.88 (BCF = 7.53e+003 L/kg wet-wt)
Biotransformation Half-Life (days) : 2.97 (normalized to 10 g fish)
Log BAF (Arnot-Gobas upper trophic): 5.55 (BAF = 3.57e+005 L/kg wet-wt)
- Endpoint:
- bioaccumulation in aquatic species: fish
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Study period:
- from 1991-12-19 to 1992-02-27
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study with acceptable restrictions
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 305 C (Bioaccumulation: Test for the Degree of Bioconcentration in Fish)
- GLP compliance:
- yes
- Radiolabelling:
- no
- Details on sampling:
- - Sampling intervals/frequency for test organisms: 1, 2, 3, 4, 6, 7 and 8 weeks
- Sample storage conditions before analysis: not mentioned
- Details on sampling and analysis of test organisms and test media samples (e.g. sample preparation, analytical methods): fish with freeze drying - Vehicle:
- yes
- Details on preparation of test solutions, spiked fish food or sediment:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: 1 g test substance + 1 g vehicle /L, no further details mentioned
- Controls: yes, blank and vehicle control
- Chemical name of vehicle (organic solvent, emulsifier or dispersant): Castor oil , ethoxylated (40 EO)
- Concentration of vehicle in test medium (stock solution and final test solution(s) including control(s)): stock solution: 1 g/L; final test solutions: same as test material, vehicle control: 0; 20 and 200 µg/L
- Evidence of undissolved material (e.g. precipitate, surface film, etc): nothing mentioned - Test organisms (species):
- Cyprinus carpio
- Details on test organisms:
- TEST ORGANISM
- Common name: Carp
- Strain: cyprinus carpio
- Source: Limnotherm, Bergheim/Niederaussen, Germany
- Age at study initiation (mean and range, SD): not mentioned
- Length at study initiation (lenght definition, mean, range and SD): 12.9 +/- 1.3 cm
- Weight at study initiation (mean and range, SD): 30.4 +/- 6.7 g
- Health status: not mentioned
- Description of housing/holding area: 260 glass aquariums, flow rate 20 l/h
- Feeding during test: yes
- Food type: Trouvit
- Amount: approx. 1 % of body weight
- Frequency: two times per day
ACCLIMATION
- Acclimation period: 14 days
- Acclimation conditions (same as test or not): The fish were kept in 260 l aquariums in flow rate.
- Type and amount of food: Trouvit, administration in an amount of approx. 0.5 - 1 % of body weight
- Feeding frequency: daily
- Health during acclimation (any mortality observed): only healthy animals used for the test - Route of exposure:
- aqueous
- Test type:
- flow-through
- Water / sediment media type:
- not specified
- Remarks:
- freshwater
- Total exposure / uptake duration:
- 8 wk
- Total depuration duration:
- 2 wk
- Hardness:
- 200 mg/L CaCO3
- Test temperature:
- 23 +/- 2 °C
- pH:
- 7.4 - 8.3
- Dissolved oxygen:
- 6.1 - 9.1 mg/L
- TOC:
- not mentioned
- Salinity:
- not mentioned
- Details on test conditions:
- TEST SYSTEM
- Test vessel: aqariums
- Type (delete if not applicable): open
- Material, size, headspace, fill volume: glass
- Aeration: Yes
- Type of flow-through (e.g. peristaltic or proportional diluter): not mentioned
- Renewal rate of test solution (frequency/flow rate): not mentioned
- No. of organisms per vessel: 50
- No. of vessels per concentration (replicates): 1
- No. of vessels per control / vehicle control (replicates): 1
- Biomass loading rate: not mentioned
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: tapewater dechlorinated with charcoal filtered
- Holding medium different from test medium: no
OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod: not mentioned
- Light intensity: not mentioned - Nominal and measured concentrations:
- nominal concentrations tested : 20 and 200 µg/L
- Reference substance (positive control):
- no
- Details on estimation of bioconcentration:
- BASIS INFORMATION
- Measured/calculated logPow: 4.73
BASIS FOR CALCULATION OF BCF
- Estimation: BCF = Concentration in Fish (mg/kg) / Concentration in Water (mg/L) - Key result
- Type:
- BCF
- Value:
- 2 000 dimensionless
- Basis:
- whole body w.w.
- Time of plateau:
- 8 wk
- Calculation basis:
- steady state
- Remarks on result:
- other: Conc.in environment / dose:20 µg/L
- Key result
- Type:
- BCF
- Value:
- 9 700 dimensionless
- Basis:
- whole body d.w.
- Time of plateau:
- 8 wk
- Calculation basis:
- steady state
- Remarks on result:
- other: Conc.in environment / dose:20 µg/L
- Key result
- Type:
- BCF
- Value:
- 54 000 dimensionless
- Basis:
- total lipid content
- Time of plateau:
- 8 wk
- Calculation basis:
- steady state
- Remarks on result:
- other: Conc.in environment / dose:20 µg/L
- Key result
- Type:
- BCF
- Value:
- 6 300 dimensionless
- Basis:
- whole body w.w.
- Time of plateau:
- 8 wk
- Calculation basis:
- steady state
- Remarks on result:
- other: Conc.in environment / dose:200 µg/L
- Key result
- Type:
- BCF
- Value:
- 28 000 dimensionless
- Basis:
- whole body d.w.
- Time of plateau:
- 8 wk
- Calculation basis:
- steady state
- Remarks on result:
- other: Conc.in environment / dose:200 µg/L
- Key result
- Type:
- BCF
- Value:
- 130 000 dimensionless
- Basis:
- total lipid content
- Time of plateau:
- 8 wk
- Calculation basis:
- steady state
- Remarks on result:
- other: Conc.in environment / dose:200 µg/L
- Key result
- Elimination:
- yes
- Parameter:
- other: BCF clear decreased
- Depuration time (DT):
- 14 d
- Details on kinetic parameters:
- not performed
- Details on results:
- - Mortality of test organisms: no mortalities were observed
- Behavioural abnormalities: not mentioned
- Mortality and/or behavioural abnormalities of control: no - Validity criteria fulfilled:
- not specified
- Conclusions:
- Fish BCF (8w) = 6300 (wet weight)
- Executive summary:
The substance was tested according to the OECD 305C guideline with the nominal concentrations of 20 and 200 μg/L. The test concentrations of 9 μg/L and 61 μg/L over the entire course of the test were calculated from the weighted mean values of the analysis. The calculated BCF values show that the substance accumulates rapidly in the fish. The following bioconcentration factors were achieved within the test period of 8 weeks :
Concentrations (nominal) BCF (8 weeks) related to wet weight dry weight total lipid content 20 µg/L 2000 9700 54000 200 µg/L 6300 28000 130000 During the subsequent 14-day release phase, a clear reduction of the substance concentration in the fish was visible. The general behavior of the exposed animals showed no differences from the controls. Food consumption was normal at all test concentrations.
Referenceopen allclose all
Concentration: 20 µg/L | Concentration: 200 µg/L | |||||
Week | BCF w.w. | BCF d.w. | BCF lipid | BCF w.w. | BCF d.w. | BCF lipid |
1 | 321 | 1580 | 5160 | 905 | 4063 | 14028 |
2 | 897 | 3985 | 17000 | 1563 | 7180 | 32190 |
3 | 1558 | 7385 | 37442 | 2593 | 12049 | 44353 |
4 | 697 | 3424 | 17091 | 2694 | 12061 | 54744 |
6 | 2593 | 12630 | 75963 | 7092 | 34195 | 142713 |
7 | 2185 | 10296 | 56000 | 6713 | 29236 | 99431 |
8 | 1481 | 6963 | 37852 | 5497 | 25623 | 131055 |
depuration | ||||||
9 | 1926 | 8741 | 43482 | 2558 | 12743 | 77967 |
10 | 1370 | 6481 | 28555 | 2169 | 11618 | 53989 |
Description of key information
The registered substance contains concentration > 0.1 % of a PBT/ vPvB compound. According to the Echa Guidance R11 related to the PBT/vPvB assessment, in that case, the registered substance has also to be considered as a PBT/vPvB substance.
Therefore, this section 5.3.1 has been completed with the available data on bioaccumulation for the relevant impurity (Dibenzyltoluene: CAS 53585-53-8).
For this relevant impurity,
- the estimated fish BCF value using QSAR BCFBAF v3.00 from EpiWin 4.00 is 7525 L/kg wet/wt, meaning that this impurity is potentially bioaccumulative.
- This result is corroborated by an experimental study following an OECD 305C guidance leading to a BCF value equal to 6300 L/kg (wet wt).
- Moreover, the BCF calculations of the three compounds tested in the OECD 309 study with Dibenzyltoluene (CAS 53585-53-8): o,m-DBT, o,o-DTPM, and the relevant impurity were performed using the US EPA EPISUITE solftware, which is considered a QSAR model prediction tool of particular relevance and interest in accordance with the ECHA guidance on Information Requirements and Chemical Safety Assessment, Chapter R11 (PBT/vPvB assessment).
Key value for chemical safety assessment
- BCF (aquatic species):
- 7 525 L/kg ww
Additional information
A calculated BCF is obtained with BCFBAF model from the EPI Suite (US-EPA), based on hydrophobicity. The result obtained corresponds to a computed log Kow of 6.5, in agreement with the experimental value of this parameter determined through an OECD 117. The experimental study confirms the calculated BCF.
The estimated BCF values is 10 280 L/kg wet-wt for the compound o,m-DBT, meaning that this compound is potentially very bioaccumulable.
The estimated BCF values is 8 513 L/kg wet-wt for the compound o,o-DTPM, meaning that this compound is potentially very bioaccumulable.
The estimated BCF values is 2 169 L/kg wet-wt for the relevant impurity of DBT substance, meaning that this compound is potentially bioaccumulable.
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.