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EC number: 248-702-8 | CAS number: 27870-92-4
- 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
Biodegradation in water: screening tests
Administrative data
Link to relevant study record(s)
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Justification for type of information:
- QSAR prediction: migrated from IUCLID 5.6
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 301 C (Ready Biodegradability: Modified MITI Test (I))
- Principles of method if other than guideline:
- Prediction is done using QSAR Toolbox version 3.3
- GLP compliance:
- not specified
- Oxygen conditions:
- not specified
- Inoculum or test system:
- other: microorganisms
- Duration of test (contact time):
- 28 d
- Parameter followed for biodegradation estimation:
- other: BOD
- Parameter:
- other: BOD
- Value:
- 0.167
- Sampling time:
- 28 d
- Remarks on result:
- other: Other details not known.
- Validity criteria fulfilled:
- not specified
- Interpretation of results:
- under test conditions no biodegradation observed
- Conclusions:
- The test substance 2-Octadecyl-1H-thioxantheno(2,1,9-def)isoquinoline-1,3(2H)-dione is estimate to be not-readily biodegradable under test conditions.
- Executive summary:
Biodegradation in water ability was predicted for the test substance 2-Octadecyl-1H-thioxantheno(2,1,9-def)isoquinoline-1,3(2H)-dione (CAS no. 27870 -92 -4) using the SSS QSAR prediction model. The ready biodegradability of the test substance 2-Octadecyl-1H-thioxantheno(2,1,9-def)
isoquinoline-1,3(2H)-dione was estimated as 0.166% in 28 days by using BOD parameter. This result indicates that 2-Octadecyl-1H-thioxantheno(2,1, 9 -def)isoquinoline-1, 3(2H)-dione was estimated to be not readily biodegradable in water.
Reference
The prediction was based on dataset comprised from the following descriptors: BOD
Estimation method: Takes average value from the 5 nearest neighbours
Domain logical expression:Result: In Domain
(((("a" or "b" or "c" or "d" ) and ("e" and ( not "f") ) ) and "g" ) and ("h" and "i" ) )
Domain logical expression index: "a"
Referential boundary: The target chemical should be classified as Aryl AND Biphenyl AND Fused carbocyclic aromatic AND Fused saturated heterocycles AND Imide AND Naphtalene AND Quinolone/ Quinolinedione/ Isoquinolinedione AND Sulfide by Organic Functional groups
Domain logical expression index: "b"
Referential boundary: The target chemical should be classified as Non-covalent interaction AND Non-covalent interaction >> DNA intercalation AND Non-covalent interaction >> DNA intercalation >> Polycyclic Aromatic Hydrocarbon and Naphthalenediimide Derivatives AND SN1 AND SN1 >> Alkylation after metabolically formed carbenium ion species AND SN1 >> Alkylation after metabolically formed carbenium ion species >> Polycyclic Aromatic Hydrocarbon and Naphthalenediimide Derivatives AND SN2 AND SN2 >> Alkylation, direct acting epoxides and related after P450-mediated metabolic activation AND SN2 >> Alkylation, direct acting epoxides and related after P450-mediated metabolic activation >> Polycyclic Aromatic Hydrocarbon and Naphthalenediimide Derivatives by DNA binding by OASIS v.1.4
Domain logical expression index: "c"
Referential boundary: The target chemical should be classified as SN1 AND SN1 >> Iminium Ion Formation AND SN1 >> Iminium Ion Formation >> Aliphatic tertiary amines by DNA binding by OECD
Domain logical expression index: "d"
Referential boundary: The target chemical should be classified as Acylation AND Acylation >> Direct Acylation Involving a Leaving group AND Acylation >> Direct Acylation Involving a Leaving group >> Acetates by Protein binding by OECD
Domain logical expression index: "e"
Referential boundary: The target chemical should be classified as Non binder, MW>500 by Estrogen Receptor Binding
Domain logical expression index: "f"
Referential boundary: The target chemical should be classified as Moderate binder, NH2 group OR Non binder, impaired OH or NH2 group OR Non binder, non cyclic structure OR Non binder, without OH or NH2 group OR Strong binder, OH group OR Weak binder, NH2 group by Estrogen Receptor Binding
Domain logical expression index: "g"
Referential boundary: The target chemical should be classified as Not calculated by Hydrolysis half-life (Kb, pH 8)(Hydrowin) ONLY
Domain logical expression index: "h"
Parametric boundary:The target chemical should have a value of Molecular weight which is >= 516 Da
Domain logical expression index: "i"
Parametric boundary:The target chemical should have a value of Molecular weight which is <= 630 Da
Description of key information
Biodegradation in water ability was predicted (SSS QSAR Prediction model, 2016) for the test substance 2-Octadecyl-1H-thioxantheno(2,1,9-def)isoquinoline-1,3(2H)-dione (CAS no. 27870-92-4) using the SSS QSAR prediction model. The ready biodegradability of the test substance 2-Octadecyl-1H-thioxantheno(2,1,9-def)isoquinoline-1,3(2H)-dione was estimated as 0.166% in 28 days by using BOD parameter. This result indicates that 2-Octadecyl-1H-thioxantheno(2,1, 9 -def)isoquinoline-1, 3(2H)-dione was estimated to be not readily biodegradable in water.
Key value for chemical safety assessment
- Biodegradation in water:
- under test conditions no biodegradation observed
Additional information
The predicted data for the test compound2-Octadecyl-1H-thioxantheno(2,1,9-def)isoquinoline-1,3(2H)-dione(CAS No. 27870-92-4) and the study for its read across substance were reviewed for the biodegradation end point which are summarized as below:
Biodegradation in water ability was predicted (SSS QSAR Prediction model, 2016) for the test substance 2-Octadecyl-1H-thioxantheno
(2,1,9-def)isoquinoline-1,3(2H)-dione (CAS no. 27870-92-4) using the SSS QSAR prediction model. The ready biodegradability of the test substance 2-Octadecyl-1H-thioxantheno(2,1,9-def)isoquinoline-1,3(2H)-dione was estimated as 0.166% in 28 days by using BOD parameter. This result indicates that 2-Octadecyl-1H-thioxantheno(2,1, 9 -def)isoquinoline-1, 3(2H)-dione was estimated to be not readily biodegradable in water.
Estimation Programs Interface Suite (EPI suite, 2016) was run to predict the biodegradation potential of the test compound 2-Octadecyl-1H- thioxantheno(2,1,9-def)isoquinoline-1,3(2H)-dione (CAS No. 27870 -92 -4). The screening test ready biodegradability of the substance was calculated using the software BIOWIN v4.10. The results indicate that 2-Octadecyl-1H-thioxantheno(2,1,9-def)isoquinoline-1,3(2H)- dione is not expected to be readily biodegradable in nature.
Biodegradation study was conducted for 15 days (K. YOSHIMURA et. al; 1980) for evaluating the percentage biodegradability of test substanceTri-n-octylamine. Biodegradation tests were carried out with an oxygen consumption measuring apparatus (Ohkura Coulometer) at 25°C. The basal medium was the JIS (Japanese Industrial Standards) BUD diluent prepared by adding 3 ml each of solution A, B, C and D to 987 ml of deionized water. The incubation chamber includes an incubation flask with a magnetic stirrer and a small vessel for carbon dioxide absorbent.Colorimetric, total organic carbon (TOC) and CO 2 production measurements. The colorimetric measurement was carried out according to Auerbach's method (Bromophenol Blue), whereas the TOC measurement was with a Beckman TOC analyzer.C02production was measured according to Ito's method. Activated sludge was obtained from a municipal sewage plant that treated domestic sewage in Tokyo. Concentration of inoculum i.e, activated sludge used was 30 mg/l and initial test substance conc. used in the study was 100 mg/l. The percentage degradation of test substance was found to be in the range of 0% by BOD/ThOD in 15 days. Thus, the substanceTri-n-octylamineis not expected to be readily biodegradable in water.
Biodegradation study was conducted (J-CHECK, 2016) for 14 days for evaluating the percentage biodegradability of test substance Tri-n-octylamine. Concentration of inoculum i.e; sludge used was 100 mg/l and initial test substance conc. used in the study was 30 mg/l. The percentage degradation of test substancewas found to be 0% by BOD and 12% by GC in 14 days. Thus, the substance Tri-n-octylamine is not expected to be readily biodegradable in water.
Biodegradation study was conducted for 14 days for evaluating the percentage biodegradability of test substanceTri-n-octylamine [Environmental Fate Data Base (EFDB), 2016]. Concentration of inoculum i.e; activated sludge used was 30 mg/l and intial test substance concentration used in the study was 100 mg/l. The percentage degradation of test substance was found to be in the range of 0-29% by BOD in 14 days at a temperature of 25°C and pH 7.0. Thus, the substance Tri-n-octylamineis not expected to be readily biodegradable in water.
On the basis of above results for target and read across substance, it can be concluded that the test substance 2-Octadecyl-1H-thioxantheno
(2,1,9-def)isoquinoline-1,3(2H)-dione can be expected to be not readily biodegradable in nature.
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