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EC number: 281-638-9 | CAS number: 84000-82-8
- 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
Biodegradation in water: screening tests
Administrative data
Link to relevant study record(s)
- Endpoint:
- biodegradation in water: screening tests
- 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 predicted using OECD QSAR toolbox version 3.3 and QMRF report has been attached
- Qualifier:
- according to guideline
- Guideline:
- other: estimated data
- Principles of method if other than guideline:
- Prediction was done by using OECD QSAR toolbox v3.3
- GLP compliance:
- not specified
- Specific details on test material used for the study:
- - Name of test material (IUPAC name): 1,4-dimethyl-5-[[4-[methylbenzylamino]phenyl]azo]-1H-1,2,4-triazolium acetate
- Common name: 1,4-dimethyl-5-[[4-[methylbenzylamino]phenyl]azo]-1H-1,2,4-triazolium acetate
- Molecular formula: C18H21N6.C2H3O2
- Molecular weight: 380.4496 g/mol
- Smiles notation: CC(=O)[O-].Cn1cn[n+](c1/N=N/c2ccc(cc2)N(C)Cc3ccccc3)C
- InChl: 1S/C18H21N6.C2H4O2/c1-22(13-15-7-5-4-6-8-15)17-11-9-16(10-12-17)20-21-18-23(2)14-19-24(18)3;1-2(3)4/h4-12,14H,13H2,1-3H3;1H3,(H,3,4)/q+1;/p-1
- Substance type: Organic - Parameter followed for biodegradation estimation:
- other: BOD
- Key result
- Parameter:
- other: BOD
- Value:
- 0.92
- Sampling time:
- 28 d
- Remarks on result:
- other: no other details
- Validity criteria fulfilled:
- not specified
- Interpretation of results:
- not readily biodegradable
- Conclusions:
- Biodegradability of test chemical 1,4-dimethyl-5-[[4-[methylbenzylamino]phenyl]azo]-1H-1,2,4-triazolium acetate (CAS no.84000-82-8) was estimated by
using OECD QSAR tool box v3.3 by considering six closest read across chemicals with log Kow as primary descriptor. 1,4-dimethyl-5-[[4-[methylbenzylamino]phenyl]azo]-1H-1,2,4-triazolium acetate undergoes 0.92% biodegradation by considering BOD as parameter and microrganisms as inoculum in 28 days. On the basis of this percent biodegradability value it can be concluded that test chemical 1,4-dimethyl-5-[[4-[methylbenzylamino]phenyl]azo]-1H-1,2,4-triazolium acetate is not readily biodegradable. - Executive summary:
Biodegradability of test chemical 1,4-dimethyl-5-[[4-[methylbenzylamino]phenyl]azo]-1H-1,2,4-triazolium acetate (CAS no.84000-82-8) was estimated by
using OECD QSAR tool box v3.3 by considering six closest read across chemicals with log Kow as primary descriptor. 1,4-dimethyl-5-[[4-[methylbenzylamino]phenyl]azo]-1H-1,2,4-triazolium acetate undergoes 0.92% biodegradation by considering BOD as parameter and microrganisms as inoculum in 28 days. On the basis of this percent biodegradability value it can be concluded that test chemical 1,4-dimethyl-5-[[4-[methylbenzylamino]phenyl]azo]-1H-1,2,4-triazolium acetate is not readily biodegradable.
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" )
and "c" )
and "d" )
and "e" )
and "f" )
and ("g"
and (
not "h")
)
)
and ("i"
and "j" )
)
Domain
logical expression index: "a"
Referential
boundary: The
target chemical should be classified as Michael addition OR Michael
addition >> P450 Mediated Activation to Quinones and Quinone-type
Chemicals OR Michael addition >> P450 Mediated Activation to Quinones
and Quinone-type Chemicals >> Arenes OR SN1 OR SN1 >> Iminium Ion
Formation OR SN1 >> Iminium Ion Formation >> Aliphatic tertiary amines
OR SN1 >> Nitrenium Ion formation OR SN1 >> Nitrenium Ion formation >>
Aromatic azo OR SN1 >> Nitrenium Ion formation >> Tertiary aromatic
amine OR SN1 >> Nitrenium Ion formation >> Unsaturated heterocyclic azo
by DNA binding by OECD ONLY
Domain
logical expression index: "b"
Referential
boundary: The
target chemical should be classified as Aliphatic Amines by Aquatic
toxicity classification by ECOSAR
Domain
logical expression index: "c"
Referential
boundary: The
target chemical should be classified as Not calculated by Biodeg BioHC
half-life (Biowin) ONLY
Domain
logical expression index: "d"
Referential
boundary: The
target chemical should be classified as weeks - months by Biodeg primary
(Biowin 4) ONLY
Domain
logical expression index: "e"
Referential
boundary: The
target chemical should be classified as Does NOT Biodegrade Fast by
Biodeg probability (Biowin 1) ONLY
Domain
logical expression index: "f"
Referential
boundary: The
target chemical should be classified as months and longer by Biodeg
ultimate (Biowin 3) ONLY
Domain
logical expression index: "g"
Referential
boundary: The
target chemical should be classified as Non binder, without OH or NH2
group by Estrogen Receptor Binding
Domain
logical expression index: "h"
Referential
boundary: The
target chemical should be classified as Non binder, MW>500 by Estrogen
Receptor Binding
Domain
logical expression index: "i"
Parametric
boundary:The
target chemical should have a value of Molecular weight which is >= 214
Da
Domain
logical expression index: "j"
Parametric
boundary:The
target chemical should have a value of Molecular weight which is <= 443
Da
Description of key information
Biodegradability of test chemical 1,4-dimethyl-5-[[4-[methylbenzylamino]phenyl]azo]-1H-1,2,4-triazolium acetate (CAS no.84000-82-8) was estimated by
using OECD QSAR tool box v3.3 by considering six closest read across chemicals with log Kow as primary descriptor. 1,4-dimethyl-5-[[4-[methylbenzylamino]phenyl]azo]-1H-1,2,4-triazolium acetate undergoes 0.92% biodegradation by considering BOD as parameter and microrganisms as inoculum in 28 days. On the basis of this percent biodegradability value it can be concluded that test chemical 1,4-dimethyl-5-[[4-[methylbenzylamino]phenyl]azo]-1H-1,2,4-triazolium acetate is not readily biodegradable.
Key value for chemical safety assessment
Additional information
Biodegradation in water :
Various predicted data for the target compound1,4-dimethyl-5-[[4-[methylbenzylamino]phenyl]azo]-1H-1,2,4-triazolium acetate ( CAS no. 84000 -82 -8) and supporting weight of evidence studies for its read across substance were reviewed for the biodegradation end point which are summarized as below:
Biodegradability of test chemical 1,4-dimethyl-5-[[4-[methylbenzylamino]phenyl]azo]-1H-1,2,4-triazolium acetate (CAS no.84000-82-8) was estimated by using OECD QSAR tool box v3.3 by considering six closest read across chemicals with log Kow as primary descriptor. 1,4-dimethyl-5-[[4-[methylbenzylamino]phenyl]azo]-1H-1,2,4-triazolium acetate undergoes 0.92% biodegradation by considering BOD as parameter and microrganisms as inoculum in 28 days. On the basis of this percent biodegradability value it can be concluded that test chemical 1,4-dimethyl-5-[[4-[methylbenzylamino]phenyl]azo]-1H-1,2,4-triazolium acetate is not readily biodegradable.
In another prediction by Estimation Programs Interface Suite (EPI suite, 2017) was run to predict the biodegradation potential of the test compound 1,4-dimethyl-5-[[4-[methylbenzylamino]phenyl]azo]-1H-1,2,4-triazolium acetate(CAS no.84000 -82 -8) in the presence of mixed populations of environmental microorganisms. The biodegradability of the substance was calculated using seven different models such as Linear Model, Non-Linear Model, Ultimate Biodegradation Timeframe, Primary Biodegradation Timeframe, MITI Linear Model, MITI Non-Linear Model and Anaerobic Model (called as Biowin 1-7, respectively) of the BIOWIN v4.10 software. The results indicate that chemical 1,4-dimethyl-5-[[4-[methylbenzylamino]phenyl]azo]-1H-1,2,4-triazolium acetate is expected to be not readily biodegradable.
The above estimated results were supported by experimental result summarized in Advisory Board for Environmentally Relevant Existing Substances (BUA), Vol. 221, Pg. no. 42, 2000 for structurally and functionally read across substance N-benzyl-N-ethylaniline (CAS: 92-59-1).
Biodegradation study was conducted for 28 days for evaluating the percentage biodegradability of test substance N-benzyl-N-ethylaniline (CAS no.92-59-1).The percentage degradation of test substance N-benzyl-N-ethylaniline was determined to be 0% by BOD parameter in 28 days. Thus, based on percentage degradation, N-benzyl-N-ethylaniline is considered to be not readily biodegradable in nature.
The above experimental data was further supported by experimental result summarized in Japan chemicals collaborative knowledge database (J-check), 2017 for structurally and functionally similar read across substance N, N-dimethylaniline (121-69-7).
Biodegradation study was conducted for 14 days for evaluating the percentage biodegradability of test substance N, N-dimethylaniline (CAS no. 121-69-7). Concentration of inoculum i.e, sludge used was 30 mg/l and initial test substance conc. used in the study was 100 mg/l, respectively. The percentage degradation of test substance N, N-dimethylaniline was determined to be1.9, 12.3 and 0% by BOD, TOC removal and GC parameter in 14 days. Thus, based on percentage degradation, N, N-dimethylaniline is considered to be not readily biodegradable in nature.
On the basis of above results for target chemical1,4-dimethyl-5-[[4-[methylbenzylamino]phenyl]azo]-1H-1,2,4-triazolium acetate(from OECD QSAR toolbox version 3.3 and EPI suite, 2017) and for its read across substance (from authoritative database J-CHECK &Advisory Board for Environmentally Relevant Existing Substancesand peer reviewed journal), it can be concluded that the test substance1,4-dimethyl-5-[[4-[methylbenzylamino]phenyl]azo]-1H-1,2,4-triazolium acetatecan be expected to be not readily biodegradable in nature.
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