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EC number: 202-334-4 | CAS number: 94-46-2
- 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:
- other information
- 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:
- The supporting QMRF report has been attached.
- 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 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): Isopentyl Benzoate
- Molecular formula: C12 H16 O2
- Molecular weight : 192.256 g/mol
- Smiles notation: c1(C(OCCC(C)C)=O)ccccc1
- InChl : 1S/C12H16O2/c1-10(2)8-9-14-12(13)11-6-4-3-5-7-11/h3-7,10H,8-9H2,1-2H3
- Substance type: organic
- Physical state: Liquid - Test organisms (species):
- Daphnia magna
- Test type:
- static
- Water media type:
- freshwater
- Total exposure duration:
- 48 h
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 18.3 mg/L
- Nominal / measured:
- estimated
- Conc. based on:
- test mat.
- Basis for effect:
- other: Intoxication
- Validity criteria fulfilled:
- not specified
- Conclusions:
- The short term toxicity on aquatic invertebrates was predicted for Isopentyl Benzoate (94-46-2). EC50 value was estimated to be 18.3 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 forIsopentyl Benzoate (94-46-2). EC50 value was estimated to be 18.3 mg/l for Daphnia magna for 48 hrs duration. Based on the value, the chemical was considered to be toxic to aquatic invertebrates but it was readily biodegradable in nature hence, can be considered to be not classified as per the CLP regulations.
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" or "e" )
and ("f"
and (
not "g")
)
)
and ("h"
and (
not "i")
)
)
and ("j"
and (
not "k")
)
)
and ("l"
and (
not "m")
)
)
and "n" )
and "o" )
and ("p"
and (
not "q")
)
)
and ("r"
and (
not "s")
)
)
and ("t"
and "u" )
)
Domain
logical expression index: "a"
Referential
boundary: The
target chemical should be classified as Esters (Acute toxicity) by
US-EPA New Chemical Categories
Domain
logical expression index: "b"
Referential
boundary: The
target chemical should be classified as Aryl AND Carboxylic acid ester
AND Isopropyl by Organic Functional groups
Domain
logical expression index: "c"
Referential
boundary: The
target chemical should be classified as Aryl AND Carboxylic acid ester
AND Isopropyl AND Overlapping groups by Organic Functional groups
(nested)
Domain
logical expression index: "d"
Referential
boundary: The
target chemical should be classified as Aliphatic Carbon [CH] AND
Aliphatic Carbon [-CH2-] AND Aliphatic Carbon [-CH3] AND Aromatic Carbon
[C] AND Carbonyl, olefinic attach [-C(=O)-] AND Carbonyl, one aromatic
attach [-C(=O)-] AND Ester, aliphatic attach [-C(=O)O] AND Miscellaneous
sulfide (=S) or oxide (=O) AND Olefinic carbon [=CH- or =C<] AND
Tertiary Carbon by Organic functional groups (US EPA)
Domain
logical expression index: "e"
Referential
boundary: The
target chemical should be classified as Aromatic compound AND Carbonic
acid derivative AND Carboxylic acid derivative AND Carboxylic acid ester
by Organic functional groups, Norbert Haider (checkmol)
Domain
logical expression index: "f"
Referential
boundary: The
target chemical should be classified as No alert found by DNA binding by
OASIS v.1.3
Domain
logical expression index: "g"
Referential
boundary: The
target chemical should be classified as AN2 OR AN2 >> Schiff base
formation by aldehyde formed after metabolic activation OR AN2 >> Schiff
base formation by aldehyde formed after metabolic activation >> Geminal
Polyhaloalkane Derivatives OR AN2 >> Shiff base formation after aldehyde
release OR AN2 >> Shiff base formation after aldehyde release >>
Specific Acetate Esters OR AN2 >> Shiff base formation for aldehydes OR
AN2 >> Shiff base formation for aldehydes >> Geminal Polyhaloalkane
Derivatives OR AN2 >> Shiff base formation for aldehydes >> Haloalkane
Derivatives with Labile Halogen OR AN2 >> Thioacylation via nucleophilic
addition after cysteine-mediated thioketene formation OR AN2 >>
Thioacylation via nucleophilic addition after cysteine-mediated
thioketene formation >> Haloalkenes with Electron-Withdrawing Groups OR
Non-covalent interaction OR Non-covalent interaction >> DNA
intercalation OR Non-covalent interaction >> DNA intercalation >> DNA
Intercalators with Carboxamide Side Chain OR Radical OR Radical >>
Radical mechanism via ROS formation (indirect) OR Radical >> Radical
mechanism via ROS formation (indirect) >> Geminal Polyhaloalkane
Derivatives OR SN1 OR SN1 >> Carbenium ion formation OR SN1 >> Carbenium
ion formation >> Alpha-Haloethers OR SN1 >> Nucleophilic attack after
carbenium ion formation OR SN1 >> Nucleophilic attack after carbenium
ion formation >> Specific Acetate Esters OR SN1 >> Nucleophilic attack
after reduction and nitrenium ion formation OR SN1 >> Nucleophilic
attack after reduction and nitrenium ion formation >> Nitrobiphenyls and
Bridged Nitrobiphenyls OR SN2 OR SN2 >> Acylation OR SN2 >> Acylation >>
Specific Acetate Esters OR SN2 >> Acylation involving a leaving group
OR SN2 >> Acylation involving a leaving group >> Geminal
Polyhaloalkane Derivatives OR SN2 >> Acylation involving a leaving group
>> Haloalkane Derivatives with Labile Halogen OR SN2 >> Acylation
involving a leaving group after metabolic activation OR SN2 >> Acylation
involving a leaving group after metabolic activation >> Geminal
Polyhaloalkane Derivatives OR SN2 >> Alkylation, direct acting epoxides
and related after P450-mediated metabolic activation OR SN2 >>
Alkylation, direct acting epoxides and related after P450-mediated
metabolic activation >> Haloalkenes with Electron-Withdrawing Groups OR
SN2 >> Alkylation, nucleophilic substitution at sp3-carbon atom OR SN2
>> Alkylation, nucleophilic substitution at sp3-carbon atom >>
Haloalkane Derivatives with Labile Halogen OR SN2 >> Direct acting
epoxides formed after metabolic activation 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 >> DNA alkylation >>
Vicinal Dihaloalkanes OR SN2 >> Internal SN2 reaction with aziridinium
and/or cyclic sulfonium ion formation (enzymatic) OR SN2 >> Internal SN2
reaction with aziridinium and/or cyclic sulfonium ion formation
(enzymatic) >> Vicinal Dihaloalkanes OR SN2 >> Nucleophilic substitution
at sp3 Carbon atom OR SN2 >> Nucleophilic substitution at sp3 Carbon
atom >> Specific Acetate Esters OR SN2 >> Nucleophilic substitution at
sp3 carbon atom after thiol (glutathione) conjugation OR SN2 >>
Nucleophilic substitution at sp3 carbon atom after thiol (glutathione)
conjugation >> Geminal Polyhaloalkane Derivatives OR SN2 >> SN2 at an
activated carbon atom OR SN2 >> SN2 at an activated carbon atom >>
Quinoline Derivatives OR SN2 >> SN2 at sp3-carbon atom OR SN2 >> SN2 at
sp3-carbon atom >> Alpha-Haloethers by DNA binding by OASIS v.1.3
Domain
logical expression index: "h"
Referential
boundary: The
target chemical should be classified as Non binder, without OH or NH2
group by Estrogen Receptor Binding
Domain
logical expression index: "i"
Referential
boundary: The
target chemical should be classified as Non binder, impaired OH or NH2
group OR Non binder, MW>500 OR Non binder, non cyclic structure OR
Strong binder, OH group OR Weak binder, NH2 group OR Weak binder, OH
group by Estrogen Receptor Binding
Domain
logical expression index: "j"
Referential
boundary: The
target chemical should be classified as No alert found by Protein
binding by OASIS v1.3
Domain
logical expression index: "k"
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
>> 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 or thiolysis OR Acylation >> Ester aminolysis or
thiolysis >> Activated aryl esters 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 Nucleophilic addition OR Nucleophilic
addition >> Addition to carbon-hetero double bonds OR Nucleophilic
addition >> Addition to carbon-hetero double bonds >> Ketones 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 >> Nucleophilic substitution at sp3 carbon atom 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 SN2 >> SN2 reaction at a sulfur atom OR SN2 >> SN2
reaction at a sulfur atom >> Thiocyanates OR SNAr OR SNAr >>
Nucleophilic aromatic substitution on activated aryl and heteroaryl
compounds OR SNAr >> Nucleophilic aromatic substitution on activated
aryl and heteroaryl compounds >> Activated aryl and heteroaryl compounds
by Protein binding by OASIS v1.3
Domain
logical expression index: "l"
Referential
boundary: The
target chemical should be classified as No alert found by Protein
binding by OECD
Domain
logical expression index: "m"
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 >> Acetates OR SN2 OR SN2 >> SN2 reaction at
sp3 carbon atom OR SN2 >> SN2 reaction at sp3 carbon atom >> Allyl
acetates and related chemicals by Protein binding by OECD
Domain
logical expression index: "n"
Referential
boundary: The
target chemical should be classified as Class 3 (unspecific reactivity)
by Acute aquatic toxicity classification by Verhaar (Modified) ONLY
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 No alert found by Protein
binding alerts for Chromosomal aberration by OASIS v1.1
Domain
logical expression index: "q"
Referential
boundary: The
target chemical should be classified as AN2 OR AN2 >> Nucleophilic
addition to pyridonimine tautomer of aminopyridoindoles or
aminopyridoimidazoles OR AN2 >> Nucleophilic addition to pyridonimine
tautomer of aminopyridoindoles or aminopyridoimidazoles >> Heterocyclic
Aromatic Amines OR Radical mechanism OR Radical mechanism >> ROS
generation and direct attack of hydroxyl radical to the C8 position of
nucleoside base OR Radical mechanism >> ROS generation and direct attack
of hydroxyl radical to the C8 position of nucleoside base >>
Heterocyclic Aromatic Amines OR SE reaction (CYP450-activated
heterocyclic amines) OR SE reaction (CYP450-activated heterocyclic
amines) >> Direct attack of arylnitrenium cation to the C8 position of
nucleoside base OR SE reaction (CYP450-activated heterocyclic amines) >>
Direct attack of arylnitrenium cation to the C8 position of nucleoside
base >> Heterocyclic Aromatic Amines OR SR reaction
(peroxidase-activated heterocyclic amines) OR SR reaction
(peroxidase-activated heterocyclic amines) >> Direct attack of
arylnitrenium radical to the C8 position of nucleoside base OR SR
reaction (peroxidase-activated heterocyclic amines) >> Direct attack of
arylnitrenium radical to the C8 position of nucleoside base >>
Heterocyclic Aromatic Amines by Protein binding alerts for Chromosomal
aberration by OASIS v1.1
Domain
logical expression index: "r"
Referential
boundary: The
target chemical should be classified as Non-Metals by Groups of elements
Domain
logical expression index: "s"
Referential
boundary: The
target chemical should be classified as Halogens by Groups of elements
Domain
logical expression index: "t"
Parametric
boundary:The
target chemical should have a value of log Kow which is >= 1.66
Domain
logical expression index: "u"
Parametric
boundary:The
target chemical should have a value of log Kow which is <= 4.61
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 five closest read across substances, the short term toxicity on aquatic invertebrates was predicted forIsopentyl Benzoate (94-46-2). EC50 value was estimated to be 18.3 mg/l for Daphnia magna for 48 hrs duration.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 18.3 mg/L
Additional information
Short term toxicity to aquatic invertebrates was summaries with two prediction studies for Isopentyl Benzoate (94-46-2) and two experimental studies with read across are 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 five closest read across substances, the short term toxicity on aquatic invertebrates was predicted forIsopentyl Benzoate (94-46-2). EC50 value was estimated to be 18.3 mg/l for Daphnia magna for 48 hrs duration.
Prediction done by EPI suite, ECOSAR version 1.1, the LC 50 value for short term toxicity to aquatic invertebrates was predicted. On the basis of this program, the LC 50 value for short term toxicity to aquatic invertebrates was predicted to be 3.004mg/l for Isopentyl Benzoate (94-46-2) in 48 hrs.Based on the value, the chemical was considered to be toxic to aquatic invertebrates but it was readily biodegradable in nature hence, can be considered to be not classified as per the CLP regulations.
Short term toxicity to aquatic invertebrates was performed in functionally related read across Benzoic acid, methyl ester (93-58-3) from High Production Volume Information System (HPVIS), 1997 according to the OECD guideline 202 in Daphnia magna for 48 hrs at different nominal concentrations as mg/L: 9.38, 18.8, 37.5, 75, 150, and 300 mg/L. The test was performed in duplicates. Freshwater and solvent controls were also tested. Ten Daphnia magna were added in pairs. After the experiment , the EC 50 value for Benzoic acid, methyl ester was determined to be 32.1 mg/l. Based on value, the Benzoic acid, methyl ester was considered to be toxic to aquatic invertebrates but as it was readily biodegradable it can considered to be not classified as per the CLP regulations.
Another functionally related read across 1-[2-(benzoyloxy)propoxy]propan-2-yl benzoate (27138-31-4) was performed in Daphnia magna from High Production Volume Information System (HPVIS),1996 for 48 hrs at different nominal concentrations as mg/L: 1.0, 2.2, 4.6, 10, 22, 46 and 100 mg/L. The test was performed in duplicates. Freshwater were used for experiment. After the experiment, the EC 50 value for 1-[2-(benzoyloxy)propoxy]propan-2-yl benzoate was determined to be 19.31 mg/l. Based on value, 1-[2-(benzoyloxy)propoxy]propan-2-yl benzoate was considered to be toxic to aquatic invertebrates but as it was readily biodegradable it can considered to be not classified as per the CLP regulations.
Based on the above data and studies of functionally related read across chemicals it can be considered that all the weight of evidence studies supported the classifications and on the basis of thatIsopentyl Benzoate (94-46-2) was considered to be toxic to aquatic invertebrates but it was readily biodegradable in nature hence, can be considered to be not classified as per the CLP regulations.
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