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EC number: 230-053-7 | CAS number: 6928-85-4
- 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:
- 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 version.3.3 and QMRF report has been attached.
- Qualifier:
- according to guideline
- Guideline:
- other: Predicted data
- Principles of method if other than guideline:
- Prediction is done using QSAR Toolbox version 3.3 with log kow as the primary discriptors.
- GLP compliance:
- not specified
- Specific details on test material used for the study:
- - Name of test material (as cited in study report): 4-Methylpiperazin-1-amine
- Molecular formula: C5H13N3
- Molecular weight: 115.179 g/mol
- Substance type: organic
- Physical state: Liquid
- Smiles notation: N1(CCN(CC1)C)N
- InChl: 1S/C5H13N3/c1-7-2-4-8(6)5-3-7/h2-6H2,1H3 - Analytical monitoring:
- no
- Vehicle:
- no
- Test organisms (species):
- Daphnia magna
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 163.39 mg/L
- Nominal / measured:
- estimated
- Conc. based on:
- test mat.
- Basis for effect:
- other: Intoxication
- Remarks on result:
- other: not toxic
- Conclusions:
- Based on the prediction done using the OECD QSAR toolbox version 3.3 with log kow as the primary descriptor and considering the five closest read across substances, the short term toxicity on aquatic invertebrates was predicted for 4-methylpiperazin-1-amine (Cas no. 6928-85-4). Effect concentration i.e EC50 value was estimated to be 163.39 mg/l for Daphnia magna for 48 hrs duration.
- 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 five closest read across substances, the short term toxicity on aquatic invertebrates was predicted for 4-methylpiperazin-1-amine (Cas no. 6928-85-4). Effect concentration i.e EC50 value was estimated to be 163.39 mg/l for Daphnia magna for 48 hrs duration. It was concluded that the 4-methylpiperazin-1-amine (Cas no. 6928-85-4) was likely to be not-toxic to aquatic invertebrates, hence it can be considered to be “not classified” as per the CLP classification criteria for aquatic environment.
Reference
The
prediction was based on dataset comprised from the following
descriptors: EC50
Estimation method: Takes average value from the 6 nearest neighbours
Domain logical expression:Result: In Domain
((((((("a"
or "b" or "c" )
and "d" )
and ("e"
and (
not "f")
)
)
and "g" )
and "h" )
and ("i"
and (
not "j")
)
)
and ("k"
and "l" )
)
Domain
logical expression index: "a"
Referential
boundary: The
target chemical should be classified as Aliphatic Amines by US-EPA New
Chemical Categories
Domain
logical expression index: "b"
Referential
boundary: The
target chemical should be classified as Radical OR Radical >> Radical
mechanism via ROS formation (indirect) OR Radical >> Radical mechanism
via ROS formation (indirect) >> Hydrazine Derivatives by DNA binding by
OASIS v.1.3 ONLY
Domain
logical expression index: "c"
Referential
boundary: The
target chemical should be classified as SN1 OR SN1 >> Iminium Ion
Formation OR SN1 >> Iminium Ion Formation >> Aliphatic tertiary amines
by DNA binding by OECD ONLY
Domain
logical expression index: "d"
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 ONLY
Domain
logical expression index: "e"
Referential
boundary: The
target chemical should be classified as No alert found by Protein
binding by OASIS v1.3
Domain
logical expression index: "f"
Referential
boundary: The
target chemical should be classified as Acylation OR Acylation >> Direct
acylation involving a leaving group OR Acylation >> Direct acylation
involving a leaving group >> Azlactones and unsaturated lactone
derivatives OR Acylation >> Direct acylation involving a leaving group
>> Carbamates OR Acylation >> Direct acylation involving a leaving
group >> N-Acylated heteroaromatic amines OR Acylation >> Direct
acylation involving a leaving group >> N-Acylsulfonamides OR Acylation
>> Ester aminolysis OR Acylation >> Ester aminolysis >> Amides OR
Acylation >> Ester aminolysis >> Dithiocarbamates OR Michael Addition OR
Michael Addition >> Michael addition on conjugated systems with electron
withdrawing group OR Michael Addition >> Michael addition on conjugated
systems with electron withdrawing group >> alpha,beta-Carbonyl compounds
with polarized double bonds OR Michael Addition >> Quinone type
chemicals OR Michael Addition >> Quinone type chemicals >> Pyranones,
Pyridones (and related nitrogen chemicals) OR Schiff base formation OR
Schiff base formation >> Pyrazolones and Pyrazolidinones derivatives OR
Schiff base formation >> Pyrazolones and Pyrazolidinones derivatives >>
Pyrazolones and Pyrazolidinones OR SN2 OR SN2 >> Interchange reaction
with sulphur containing compounds OR SN2 >> Interchange reaction with
sulphur containing compounds >> Thiols and disulfide compounds OR SN2
>> Nucleophilic substitution at sp3 carbon atom OR SN2 >> Nucleophilic
substitution at sp3 carbon atom >> (Thio)Phosphates OR SN2 >>
Nucleophilic substitution at sp3 carbon atom >> Alkyl halides OR SN2 >>
Nucleophilic substitution at sp3 carbon atom >> alpha-Activated
haloalkanes OR SN2 >> Nucleophilic substitution on benzilyc carbon atom
OR SN2 >> Nucleophilic substitution on benzilyc carbon atom >>
alpha-Activated benzyls OR SN2 >> SN2 Reaction at a sp3 carbon atom OR
SN2 >> SN2 Reaction at a sp3 carbon atom >> Activated alkyl esters and
thioesters OR SNVinyl OR SNVinyl >> SNVinyl at a vinylic (sp2) carbon
atom OR SNVinyl >> SNVinyl at a vinylic (sp2) carbon atom >> Vinyl type
compounds with electron withdrawing groups by Protein binding by OASIS
v1.3
Domain
logical expression index: "g"
Referential
boundary: The
target chemical should be classified as Class 5 (Not possible to
classify according to these rules) by Acute aquatic toxicity
classification by Verhaar (Modified) ONLY
Domain
logical expression index: "h"
Referential
boundary: The
target chemical should be classified as Reactive unspecified by Acute
aquatic toxicity MOA by OASIS ONLY
Domain
logical expression index: "i"
Referential
boundary: The
target chemical should be classified as Non-Metals by Groups of elements
Domain
logical expression index: "j"
Referential
boundary: The
target chemical should be classified as Alkali Earth OR Halogens by
Groups of elements
Domain
logical expression index: "k"
Parametric
boundary:The
target chemical should have a value of log Kow which is >= -2.64
Domain
logical expression index: "l"
Parametric
boundary:The
target chemical should have a value of log Kow which is <= -0.678
Description of key information
Using the OECD QSAR toolbox version 3.3 with log kow as the primary descriptor and considering the five closest read across substances, the short term toxicity on aquatic invertebrates was predicted for 4-methylpiperazin-1-amine (Cas no. 6928-85-4). Effect concentration i.e EC50 value was estimated to be 163.39 mg/l for Daphnia magna for 48 hrs duration. It was concluded that the 4-methylpiperazin-1-amine (Cas no. 6928-85-4) was likely to be not-toxic to aquatic invertebrates, hence it can be considered to be “not classified” as per the CLP classification criteria for aquatic environment.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 163.39 mg/L
Additional information
Four studies including predicted data from validated tools and experimental data from peer reviewed journal for toxicity to aquatic invertebrate endpoint of test chemical 4-methylpiperazin-1-amine (Cas no. 6928-85-4) with relevant read across which is close to target using log Kow as primary descriptor were summarised as follows:
Using the OECD QSAR toolbox version 3.3 with log kow as the primary descriptor and considering the five closest read across substances, the short term toxicity on aquatic invertebrates was predicted for 4-methylpiperazin-1-amine (Cas no. 6928-85-4). Effect concentration i.e EC50 value was estimated to be 163.39 mg/l for Daphnia magna for 48 hrs duration. It was concluded that the 4-methylpiperazin-1-amine (Cas no. 6928-85-4) was likely to be not-toxic to aquatic invertebrates, hence it can be considered to be“not classified”as per the CLP classification criteria for aquatic environment.
Similar prediction done by Using the EPI Suite ECOSAR version 1.11, the LC50 value for short term toxicity to aquatic invertebrate was predicted to be 406.90 mg/l for 4-methylpiperazin-1-amine in 48 hrs. Based on the LC50 value, it can be concluded that the substance 4-methylpiperazin-1-amine is not toxic.
Above predicted results for target is assisted by experimental data of read across chemicalN,N-dimethylformamide(Cas no. 68-12-2) from handbook,The Lethal concentration to 50% (LC50) of Crangon crangon is 100 mg/l at 48 h. On the basis of the value it can be concluded that the N,N-dimethylformamide is not toxic to the aquatic environment.
Another experimental data of read acrossN,N-dimethylformamide (Cas no. 68-12-2) from Archives of Environmental Contamination and Toxicology 1983 indicates that the lethal concentration LC50 for daphnia magna at 48 hrs is 12350 mg/l. It can be concluded that the N,N-dimethylformamide is not toxic to aquatic environment.
Thus based on the effect concentrations which is in the range100mg/l to12350give the conclusion that test substance 4-methylpiperazin-1-amine (Cas no. 6928-85-4) was likely to be non-toxic to aquatic invertebrate at environmentally relevant concentrations and can be considered to be“not classified”as per the CLP classification criteria.
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