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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

Short-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- (Q)SAR
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Justification for type of information:
- QSAR prediction: migrated from IUCLID 5.6
- Qualifier:
- according to guideline
- Guideline:
- other: as mentioned below
- Principles of method if other than guideline:
- Prediction is done using QSAR Toolbox version 3.3
- GLP compliance:
- not specified
- Test organisms (species):
- Daphnia magna
- Test type:
- static
- Water media type:
- freshwater
- Total exposure duration:
- 48 h
- Test temperature:
- 18 - 22 °C, ± 1 °C constant
- pH:
- 7.85 test initial
7.83 - 7.85 end of test - Dissolved oxygen:
- 8.28 mg/L initial test
8.20 - 8.35 mg/L end of test - Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 93.72 mg/L
- Nominal / measured:
- estimated
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Validity criteria fulfilled:
- not specified
- Conclusions:
- The predicted data suggests the effective concentration (EC50) for the 6-Chlorohexan-2-one was estimated to be 93.720046997 mg/L on the basis of mobility.
- Executive summary:
48 hrs aquatic toxicity study (SSS QSAR prediction model, 2016) was conducted to assess toxic effects of the 2-Octadecyl-1H-thioxantheno(2,1,9-def)isoquinoline-1,3(2H)-dione (CAS no 27870-92-4) and the results were predicted. The study was based on the effects of the test compound on the Daphnia magna in a static fresh water system. The predicted data suggests the effective concentration (EC50) for the 6-Chlorohexan-2-one was estimated to be 93.720046997 mg/Lon the basis of mobility.
Thus based on this value, it can be concluded that the substance can be considered as toxic to aquatic organisms. Since the substance has a molecular weight of 555.823 g/mol , by speculation, the molecular size of the test substance was so large that reduce the intake rate of chemical into tissues of aquatic biota. Hence, based on this it can be considered that the chemical was not likely to be toxic to aquatic invertebrates at environmentally relevant concentrations and can be classified as non- hazardous as per the criteria of CLP regulation
Reference
The
prediction was based on dataset comprised from the following
descriptors: EC50
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"
and (
not "j")
)
)
and "k" )
and ("l"
and (
not "m")
)
)
and "n" )
and ("o"
and "p" )
)
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
Moderate binder, OH grooup 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, NH2 group OR Strong binder, OH group OR Very strong
binder, OH 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 7)(Hydrowin) ONLY
Domain
logical expression index: "h"
Referential
boundary: The
target chemical should be classified as No superfragment by
Superfragments ONLY
Domain
logical expression index: "i"
Referential
boundary: The
target chemical should be classified as No alert found by Protein
binding alerts for Chromosomal aberration by OASIS v.1.2
Domain
logical expression index: "j"
Referential
boundary: The
target chemical should be classified as Acylation OR Acylation >>
(Thio)carbamoylation of protein nucleophiles OR Acylation >>
(Thio)carbamoylation of protein nucleophiles >> Isocyanates and
Diisocyanates OR AN2 OR AN2 >> Michael addition to activated double
bonds OR AN2 >> Michael addition to activated double bonds >> alpha,
beta - Unsaturated Carbonyls and Related Compounds OR AN2 >> Michael
addition to activated double bonds in heterocyclic ring systems OR AN2
>> Michael addition to activated double bonds in heterocyclic ring
systems >> Pyrazolone and Pyrazolidine Derivatives OR AN2 >> Michael
addition to the quinoid type structures OR AN2 >> Michael addition to
the quinoid type structures >> N-Subsituted Aromatic Amines OR AN2 >>
Shiff base formation with carbonyl compounds OR AN2 >> Shiff base
formation with carbonyl compounds >> Pyrazolone and Pyrazolidine
Derivatives by Protein binding alerts for Chromosomal aberration by
OASIS v.1.2
Domain
logical expression index: "k"
Referential
boundary: The
target chemical should be classified as Does NOT Biodegrade Fast by
Biodeg probability (Biowin 7) ONLY
Domain
logical expression index: "l"
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: "m"
Referential
boundary: The
target chemical should be classified as No alert found by Protein
binding by OECD
Domain
logical expression index: "n"
Referential
boundary: The
target chemical should be classified as Discrete chemical by Substance
Type ONLY
Domain
logical expression index: "o"
Parametric
boundary:The
target chemical should have a value of log Kow which is >= 7.66
Domain
logical expression index: "p"
Parametric
boundary:The
target chemical should have a value of log Kow which is <= 16
Description of key information
Key value for chemical safety assessment
Additional information
Various predicted studies for the 2-Octadecyl-1H-thioxantheno(2,1,9-def)isoquinoline-1,3(2H)-dionewere reviewed to summarize the following information:
48 hrs aquatic toxicity study (SSS QSAR prediction model, 2016) was conducted to assess toxic effects of the 2-Octadecyl-1H-thioxantheno(2,1,9-def)isoquinoline-1,3(2H)-dione (CAS no 27870-92-4) and the results were predicted. The study was based on the effects of the test compound on the Daphnia magna in a static fresh water system. The predicted data suggests the effective concentration (EC50) for the 6-Chlorohexan-2-one was estimated to be 93.720046997 mg/Lon the basis of mobility.
48 hrs aquatic toxicity study (EPI suite, ECOSAR version 1.1, 2016) was conducted to assess toxic effects of the 2-Octadecyl-1H-thioxantheno (2, 1, 9-def) isoquinoline-1, 3(2H)-dione (CAS no 27870-92-4) and the results were predicted. The study was based on the effects of the test compound on the Daphnia magna in a static fresh water system. The predicted data suggests the lethal concentration (LC50) for the 2-Octadecyl-1H-thioxantheno (2, 1, 9 -def) isoquinoline-1, 3(2H)-dione was estimated to be 0.000000127 mg/Lon the basis of mobility.
Thus based on above value, it can be concluded that the substance can be considered as toxic to aquatic organisms. Since the substance has a molecular weight of 555.823 g/mol, by speculation, the molecular size of the test substance was so large that reduce the intake rate of chemical into tissues of aquatic biota. Hence, based on this it can be considered that the chemical was not likely to be toxic to aquatic invertebrates at environmentally relevant concentrations and can be classified as non- hazardous as per the criteria of CLP regulation
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