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EC number: 211-932-4 | CAS number: 713-95-1
- 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, other
- Type of information:
- calculation (if not (Q)SAR)
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- accepted calculation method
- Justification for type of information:
- Estimated data generated using the EPI Suite program developed by the USEPA.
- Qualifier:
- according to guideline
- Guideline:
- other: Modeling database
- Principles of method if other than guideline:
- Prediction done using BCFBAF (v3.01) model
- GLP compliance:
- not specified
- Radiolabelling:
- not specified
- Vehicle:
- not specified
- Test organisms (species):
- other: Fish
- Route of exposure:
- aqueous
- Test type:
- not specified
- Water / sediment media type:
- natural water: freshwater
- Test temperature:
- 25 deg.C
- Reference substance (positive control):
- not specified
- Key result
- Temp.:
- 25 °C
- Type:
- BCF
- Value:
- 102.1 L/kg
- Basis:
- whole body w.w.
- Calculation basis:
- other: estimated
- Remarks on result:
- other: Non-bioaccumulative
- Validity criteria fulfilled:
- not specified
- Conclusions:
- The bioconcentration factor (BCF) of test chemical was estimated to be 102.1 L/kg whole body w.w (at 25 deg C) which does not exceed the bio concentration threshold of 2000, indicating that the test chemical is not expected to bioaccumulate in the food chain.
- Executive summary:
BCFBAF model of Estimation Programs Interface was used to predict the bioconcentration factor (BCF) of test chemical. The bioconcentration factor (BCF) of test chemical was estimated to be 102.1 L/kg whole body w.w (at 25 deg C) which does not exceed the bio concentration threshold of 2000, indicating that the test chemical is not expected to bioaccumulate in the food chain.
Reference
BCFBAF Program (v3.01) Results:
==============================
SMILES : O=C(OC(CC1)CCCCCCC)C1
CHEM : 2H-Pyran-2-one, 6-heptyltetrahydro-
MOL FOR: C12 H22 O2
MOL WT : 198.31
--------------------------------- BCFBAF v3.01 --------------------------------
Summary Results:
Log BCF (regression-based estimate): 2.01 (BCF = 102 L/kg wet-wt)
Biotransformation Half-Life (days) : 0.102 (normalized to 10 g fish)
Log BAF (Arnot-Gobas upper trophic): 1.59 (BAF = 39.1 L/kg wet-wt)
Log Kow (experimental): not available from database
Log Kow used by BCF estimates: 3.55
Equation Used to Make BCF estimate:
Log BCF = 0.6598 log Kow - 0.333 + Correction
Correction(s): Value
No Applicable Correction Factors
Estimated Log BCF = 2.009 (BCF = 102.1 L/kg wet-wt)
Description of key information
BCFBAF model of Estimation Programs Interface was used to predict the bioconcentration factor (BCF) of test chemical (2018). The bioconcentration factor (BCF) of test chemical was estimated to be 102.1 L/kg whole body w.w (at 25 deg C) which does not exceed the bio concentration threshold of 2000, indicating that the test chemical is not expected to bioaccumulate in the food chain.
Key value for chemical safety assessment
- BCF (aquatic species):
- 102.1 L/kg ww
Additional information
Various predicted data of the test chemical and supporting weight of evidence studies for its structurally similar read across substance were reviewed for the bioaccumulation end point which are summarized as below:
In aprediction done using theBCFBAF Programof Estimation Programs Interface was used to predict the bioconcentration factor (BCF) of test chemical. The bioconcentration factor (BCF) of test chemical was estimated to be 102.1 L/kg whole body w.w (at 25 deg C).
In an another prediction done by using Bio-concentration Factor (v12.1.0.50374) moduleACD (Advanced Chemistry Development)/I-Lab predictive module, 2017), theBio-concentration Factor of the test chemical was estimated to be 260 at pH range 1-14, respectively.
SciFinder database (American Chemical Society (ACS), 2017) was used for predicting the bioconcentration factor (BCF) of test chemical. The bioconcentration factor (BCF) of test chemical was estimated to be 264 at pH range 1-10 respectively (at 25 deg C).
From CompTox Chemistry Dashboard using OPERA (OPEn (quantitative) structure-activity Relationship Application) V1.02 model in which calculation based on PaDEL descriptors (calculate molecular descriptors and fingerprints of chemical), the bioaccumulation i.e BCF for test chemical was estimated to be 10.8 dimensionless . The predicted BCF result based on the 5 OECD principles.
In a supporting weight of evidence study from authoritative database (HSDB, 2017) for the test chemical, the bioaccumulation experiment was conducted in fish for estimating the BCF (bioaccumulation factor) value of test chemical. The bioaccumulation factor (BCF) value was calculated using an estimated log Kow of 2.83 and a regression derived equation. The BCF (bioaccumulation factor) value test substance in fish was determined to be 34 dimensionless.
For the test chemical, the bioaccumulation study was conducted for estimating the BCF (bioaccumulation factor) value of test chemical (authoritative database, 2017). The bioaccumulation factor (BCF) value was calculated using an estimated log Kow of 3.32 and a regression derived equation. The BCF (bioaccumulation factor) value test substance was determined to be 72 dimensionless.
On the basis of above results for test chemical, it can be concluded that the BCF value of test chemical was evaluated to be ranges from10.8 to 264, respectively,which does not exceed the bioconcentration threshold of 2000, indicating that the test chemical is not expected to bioaccumulate in the food chain.
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