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EC number: 235-424-7 | CAS number: 12224-98-5
- 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
Toxicity to aquatic algae and cyanobacteria
Administrative data
Link to relevant study record(s)
- Endpoint:
- toxicity to aquatic algae and cyanobacteria
- 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 limited documentation / justification
- Justification for type of information:
- data is from OECD QSAR toolbox v3.3 and the QMRF report has been attached
- Qualifier:
- according to guideline
- Guideline:
- other: Estimated data
- Principles of method if other than guideline:
- Prediction was done using OECD QSAR toolbox v3.3
- GLP compliance:
- not specified
- Specific details on test material used for the study:
- - Name of test material (as cited in study report): C.I. Pigment red 81
- IUPAC name: Xanthylium, 9-[2-(ethoxycarbonyl)phenyl]-3,6-bis(ethylamino)-2,7-dimethyl-, molybdatetungstatephosphate
- Molecular formula: C28H31N2O3.x-Unspecified
- Molecular weight: 443.5639 g/mol
- Smiles: CCNc1cc2c(cc1C)c(c3cc(c(cc3[o+]2)NCC)C)c4ccccc4C(=O)OCC
- InChI: 1S/C28H31N2O3/c1-6-29-23-15-25-21(13-17(23)4)27(19-11-9-10-12-20(19)28(31)32-8-3)22-14-18(5)24(30-7-2)16-26(22)33-25/h9-16, 29-30H,6-8H2,1-5H3/q+1
- Substance type: Organic
- Physical state: Solid powder (dark pink) - Analytical monitoring:
- not specified
- Details on sampling:
- no data available
- Vehicle:
- not specified
- Details on test solutions:
- no data available
- Test organisms (species):
- Desmodesmus subspicatus (previous name: Scenedesmus subspicatus)
- Details on test organisms:
- no data available
- Test type:
- static
- Water media type:
- freshwater
- Total exposure duration:
- 72 h
- Remarks on exposure duration:
- no data available
- Post exposure observation period:
- no data available
- Hardness:
- no data available
- Test temperature:
21.9 °C- pH:
- 7.9- 9.4
- Dissolved oxygen:
- no data available
- Salinity:
- no data available
- Conductivity:
- no data available
- Nominal and measured concentrations:
- no data available
- Details on test conditions:
- no data available
- Reference substance (positive control):
- not specified
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 215.213 mg/L
- Nominal / measured:
- estimated
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Remarks on result:
- other: not toxic
- Details on results:
- no data available
- Results with reference substance (positive control):
- no data available
- Reported statistics and error estimates:
- no data available
- Validity criteria fulfilled:
- not specified
- Conclusions:
- Based on the prediction done using the OECD QSAR toolbox version 3.3 with log kow as the primary descriptor and considering the closest read across substances, the toxicity to aquatic algae was predicted Xanthylium, 9-[2-(ethoxycarbonyl)phenyl]-3,6-bis(ethylamino)-2,7-dimethyl-, molybdatetungstatephosphate (CAS:12224-98-5). EC50 effecttive concentration value was estimated to be 215.213 mg/l for Desmodesmus subspicatus for 72 hrs duration. It was concluded that Xanthylium, 9-[2-(ethoxycarbonyl)phenyl]-3,6-bis(ethylamino)-2,7-dimethyl-, molybdatetungstatephosphate (CAS:12224-98-5) was likely to be not toxic to aquatic algae.
- Executive summary:
Based on the prediction done using the OECD QSAR toolbox version 3.3 with log kow as the primary descriptor and considering the closest read across substances, the toxicity to aquatic algae was predicted Xanthylium, 9-[2-(ethoxycarbonyl)phenyl]-3,6-bis(ethylamino)-2,7-dimethyl-, molybdatetungstatephosphate (CAS:12224-98-5). EC50 effecttive concentration value was estimated to be 215.213 mg/l for Desmodesmus subspicatus for 72 hrs duration. It was concluded that Xanthylium, 9-[2-(ethoxycarbonyl)phenyl]-3,6-bis(ethylamino)-2,7-dimethyl-, molybdatetungstatephosphate (CAS:12224-98-5) was likely to be not toxic to aquatic algae.
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 (
not "h")
)
)
and ("i"
and (
not "j")
)
)
and ("k"
and (
not "l")
)
)
and ("m"
and (
not "n")
)
)
and "o" )
and ("p"
and (
not "q")
)
)
and ("r"
and (
not "s")
)
)
and ("t"
and (
not "u")
)
)
and "v" )
and ("w"
and (
not "x")
)
)
and ("y"
and "z" )
)
Domain
logical expression index: "a"
Referential
boundary: The
target chemical should be classified as Esters (Chronic toxicity) by
US-EPA New Chemical Categories
Domain
logical expression index: "b"
Referential
boundary: The
target chemical should be classified as SN1 AND SN1 >> Nitrenium Ion
formation AND SN1 >> Nitrenium Ion formation >> Secondary aromatic amine
by DNA binding by OECD
Domain
logical expression index: "c"
Referential
boundary: The
target chemical should be classified as Esters by Acute aquatic toxicity
MOA by OASIS
Domain
logical expression index: "d"
Referential
boundary: The
target chemical should be classified as Esters by Aquatic toxicity
classification by ECOSAR
Domain
logical expression index: "e"
Referential
boundary: The
target chemical should be classified as No alert found by DNA binding by
OASIS v.1.3
Domain
logical expression index: "f"
Referential
boundary: The
target chemical should be classified as AN2 OR AN2 >> Michael-type
addition, quinoid structures OR AN2 >> Michael-type addition, quinoid
structures >> Quinoneimines OR AN2 >> Michael-type addition on alpha,
beta-unsaturated carbonyl compounds OR AN2 >> Michael-type addition on
alpha, beta-unsaturated carbonyl compounds >> Four- and Five-Membered
Lactones OR AN2 >> Nucleophilic addition to alpha, beta-unsaturated
carbonyl compounds OR AN2 >> Nucleophilic addition to alpha,
beta-unsaturated carbonyl compounds >> alpha, beta-Unsaturated Aldehydes
OR AN2 >> Schiff base formation OR AN2 >> Schiff base formation >>
alpha, beta-Unsaturated Aldehydes OR AN2 >> Shiff base formation after
aldehyde release OR AN2 >> Shiff base formation after aldehyde release
>> Specific Acetate Esters OR Non-covalent interaction OR Non-covalent
interaction >> DNA intercalation OR Non-covalent interaction >> DNA
intercalation >> Coumarins OR Radical OR Radical >> Generation of
reactive oxygen species OR Radical >> Generation of reactive oxygen
species >> Thiols OR Radical >> Radical mechanism via ROS formation
(indirect) OR Radical >> Radical mechanism via ROS formation (indirect)
>> Coumarins OR Radical >> ROS formation after GSH depletion (indirect)
OR Radical >> ROS formation after GSH depletion (indirect) >>
Quinoneimines OR SN1 OR SN1 >> Nucleophilic attack after carbenium ion
formation OR SN1 >> Nucleophilic attack after carbenium ion formation >>
Specific Acetate Esters OR SN2 OR SN2 >> Acylation OR SN2 >> Acylation
>> Specific Acetate Esters OR SN2 >> Alkylation, nucleophilic
substitution at sp3-carbon atom OR SN2 >> Alkylation, nucleophilic
substitution at sp3-carbon atom >> Sulfonates and Sulfates OR SN2 >>
Alkylation, ring opening SN2 reaction OR SN2 >> Alkylation, ring opening
SN2 reaction >> Four- and Five-Membered Lactones OR SN2 >> Direct acting
epoxides formed after metabolic activation OR SN2 >> Direct acting
epoxides formed after metabolic activation >> Coumarins OR SN2 >> Direct
acting epoxides formed after metabolic activation >> Quinoline
Derivatives OR SN2 >> DNA alkylation OR SN2 >> DNA alkylation >>
Alkylphosphates, Alkylthiophosphates and Alkylphosphonates OR SN2 >>
Nucleophilic substitution at sp3 Carbon atom OR SN2 >> Nucleophilic
substitution at sp3 Carbon atom >> Specific Acetate Esters OR SN2 >> SN2
at an activated carbon atom OR SN2 >> SN2 at an activated carbon atom >>
Quinoline Derivatives by DNA binding by OASIS v.1.3
Domain
logical expression index: "g"
Referential
boundary: The
target chemical should be classified as SN1 AND SN1 >> Nitrenium Ion
formation AND SN1 >> Nitrenium Ion formation >> Secondary aromatic amine
by DNA binding by OECD
Domain
logical expression index: "h"
Referential
boundary: The
target chemical should be classified as Michael addition by DNA binding
by OECD
Domain
logical expression index: "i"
Referential
boundary: The
target chemical should be classified as Not possible to classify
according to these rules by DPRA Cysteine peptide depletion
Domain
logical expression index: "j"
Referential
boundary: The
target chemical should be classified as High reactive >>
alpha,beta-carbonyl compounds with polarized multiple bonds by DPRA
Cysteine peptide depletion
Domain
logical expression index: "k"
Referential
boundary: The
target chemical should be classified as Non binder, without OH or NH2
group by Estrogen Receptor Binding
Domain
logical expression index: "l"
Referential
boundary: The
target chemical should be classified as Non binder, MW>500 by Estrogen
Receptor Binding
Domain
logical expression index: "m"
Referential
boundary: The
target chemical should be classified as Non binder, without OH or NH2
group by Estrogen Receptor Binding
Domain
logical expression index: "n"
Referential
boundary: The
target chemical should be classified as Strong binder, OH group by
Estrogen Receptor Binding
Domain
logical expression index: "o"
Referential
boundary: The
target chemical should be classified as Esters by Acute aquatic toxicity
MOA by OASIS ONLY
Domain
logical expression index: "p"
Referential
boundary: The
target chemical should be classified as Esters by Aquatic toxicity
classification by ECOSAR
Domain
logical expression index: "q"
Referential
boundary: The
target chemical should be classified as Inorganic Compound by Aquatic
toxicity classification by ECOSAR
Domain
logical expression index: "r"
Referential
boundary: The
target chemical should be classified as Esters by Aquatic toxicity
classification by ECOSAR
Domain
logical expression index: "s"
Referential
boundary: The
target chemical should be classified as Vinyl/Allyl Esters by Aquatic
toxicity classification by ECOSAR
Domain
logical expression index: "t"
Referential
boundary: The
target chemical should be classified as Alkyl substituent on aromatic
ring AND Aromatic amine [-NH2 or -NH-] AND Aromatic ether
[-O-aromatic carbon] AND Aromatic-CH AND Aromatic-CH3 AND Aromatic-H
AND Benzene AND -CH2- [linear] AND Ester [-C(=O)-O-C] AND Methyl
[-CH3] AND Number of fused 6-carbon aromatic rings AND Polycyclic -CH3
(3 fused rings or less) by Bioaccumulation - metabolism alerts
Domain
logical expression index: "u"
Referential
boundary: The
target chemical should be classified as Unsubstituted Cycloalkane OR
Unsubstituted phenyl group (C6H5-) by Bioaccumulation - metabolism alerts
Domain
logical expression index: "v"
Referential
boundary: The
target chemical should be classified as Fast by Bioaccumulation -
metabolism half-lives ONLY
Domain
logical expression index: "w"
Referential
boundary: The
target chemical should be classified as Aromatic mono-and dialkylamine
(Genotox) AND Structural alert for genotoxic carcinogenicity by
Carcinogenicity (genotox and nongenotox) alerts by ISS
Domain
logical expression index: "x"
Referential
boundary: The
target chemical should be classified as Phtalate (or buthyl) diesters
and monoesters (Nongenotox) by Carcinogenicity (genotox and nongenotox)
alerts by ISS
Domain
logical expression index: "y"
Parametric
boundary:The
target chemical should have a value of log Kow which is >= 6.27
Domain
logical expression index: "z"
Parametric
boundary:The
target chemical should have a value of log Kow which is <= 10.1
Description of key information
Based on the prediction done using the OECD QSAR toolbox version 3.3 with log kow as the primary descriptor and considering the closest read across substances, the toxicity to aquatic algae was predicted Xanthylium, 9-[2-(ethoxycarbonyl)phenyl]-3,6-bis(ethylamino)-2,7-dimethyl-, molybdatetungstatephosphate (CAS:12224-98-5). EC50 effecttive concentration value was estimated to be 215.213 mg/l for Desmodesmus subspicatus for 72 hrs duration. It was concluded that Xanthylium, 9-[2-(ethoxycarbonyl)phenyl]-3,6-bis(ethylamino)-2,7-dimethyl-, molybdatetungstatephosphate (CAS:12224-98-5) was likely to be not toxic to aquatic algae.
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 215.213 mg/L
Additional information
Following studies include the predicted data and experimental study for the target chemical and structurally similar read across to conclude the toxicity extent of Xanthylium, 9-[2-(ethoxycarbonyl)phenyl]-3,6-bis(ethylamino)-2,7-dimethyl-, molybdatetungstatephosphate (CAS:12224-98-5) towards aquatic algae is summarized as follows:
Based on the prediction done using the OECD QSAR toolbox version 3.3 with log kow as the primary descriptor and considering the closest read across substances, the toxicity to aquatic algae was predicted Xanthylium, 9-[2-(ethoxycarbonyl)phenyl]-3,6-bis(ethylamino)-2,7-dimethyl-, molybdatetungstatephosphate (CAS:12224-98-5). EC50 effecttive concentration value was estimated to be 215.213 mg/l for Desmodesmus subspicatus for 72 hrs duration. It was concluded that Xanthylium, 9-[2-(ethoxycarbonyl)phenyl]-3,6-bis(ethylamino)-2,7-dimethyl-, molybdatetungstatephosphate (CAS:12224-98-5) was likely to be not toxic to aquatic algae.
The above predicted study of target chemical is supported by the experimental study of read across chemical Fluorescein sodium; disodium 3-oxo-3H-spiro[2-benzofuran-1,9'-xanthene]-3',6'-diolate (CAS: 518-47-8) from the Lab report UERL 2017, suggests that The effect of test itemDisodium 2-(3-oxo-6-oxidoxanthen-9-yl) benzoate, CAS No. 518-47-8 was studied on the growth of fresh water green alga Chlorella vulgaris. The study was conducted following OECD guideline 201- Alga, growth inhibition test. The test concentration chosen for the study were 6.25mg/l, 12.5mg/l, 25mg/l, 50mg/l, 100mg/l and 200mg/l. The test concentrations were prepared using stock solution of the test item using mineral media. The green alga was exposed to the test concentration for a period of 72 hours to observe average specific growth rate and % growth inhibition under the effect of the test item. EC50 calculated graphically through probit analysis was observed to be 209.24 mg/l.
Thus, based on the EC50 value, test substancecan be considered asnon-toxic to aquatic organisms and thus cannot be classified as hazardous as per the CLP criteria.
Thus based on the effect concentrations which is in the range 209.24 mg/L to 215.21 mg/l give the conclusion that test substance Xanthylium, 9-[2-(ethoxycarbonyl)phenyl]-3,6-bis(ethylamino)-2,7-dimethyl-, molybdatetungstatephosphate (CAS:12224-98-5) was likely to be not toxic to aquatic algae at environmentally relevant concentrations and applying weight of evidence it can be considered to be“not classified”as per the CLP classification criteria
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