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EC number: 200-068-3 | CAS number: 50-85-1
- 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 version 3.3 and the QMRF report has been attached.
- Qualifier:
- according to guideline
- Guideline:
- other: Estimated data
- Version / remarks:
- No data available
- Deviations:
- not specified
- Principles of method if other than guideline:
- Prediction was done using the OECD QSAR toolbox version 3.3.
- GLP compliance:
- not specified
- Specific details on test material used for the study:
- Name of test material : 2-hydroxy-p-toluic acid (m cresotic acid)
Molecular formula :C8H8O3
Molecular weight :152.148 g/mol
Smiles notation :Cc1ccc(c(c1)O)C(=O)O
InChl :1S/C8H8O3/c1-5-2-3-6(8(10)11)7(9)4-5/h2-4,9H,1H3,(H,10,11)
Substance Type: Organic
Physical State: Solid - 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:
- No data available
- pH:
- 8.2
- Dissolved oxygen:
- No data available
- Salinity:
- No data available
- Conductivity:
- No data available
- Nominal and measured concentrations:
- nominal
- Details on test conditions:
- No data available
- Reference substance (positive control):
- not specified
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 112.815 mg/L
- Nominal / measured:
- estimated
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Remarks on result:
- other: from QSAR
- 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:
- The EC50 value was estimated to be 112.814 mg/l when 2-hydroxy-p-toluic acid (m cresotic acid) exposed to Desmodesmus subspicatus for 72 hrs
- Executive summary:
Based on the prediction done using the OECD QSAR toolbox version 3.4 with log kow as the primary descriptor and considering the five closest read across substances, toxicity on Desmodesmus subspicatus (previous name: Scenedesmus subspicatus)was predicted for2-hydroxy-p-toluic acid (m cresotic acid) (50-85-1).The EC50 value was estimated to be 112.814 mg/l when 2-hydroxy-p-toluic acid (m cresotic acid) exposed to Desmodesmus subspicatus for 72 hrs.
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" or "d" or "e" )
and ("f"
and (
not "g")
)
)
and ("h"
and (
not "i")
)
)
and "j" )
and ("k"
and (
not "l")
)
)
and ("m"
and (
not "n")
)
)
and ("o"
and (
not "p")
)
)
and ("q"
and "r" )
)
Domain
logical expression index: "a"
Referential
boundary: The
target chemical should be classified as m,p - Cresols by OECD HPV
Chemical Categories
Domain
logical expression index: "b"
Referential
boundary: The
target chemical should be classified as Phenols (Acute toxicity) by
US-EPA New Chemical Categories
Domain
logical expression index: "c"
Referential
boundary: The
target chemical should be classified as Weak binder, OH group by
Estrogen Receptor Binding
Domain
logical expression index: "d"
Referential
boundary: The
target chemical should be classified as Class 2 (less inert compounds)
by Acute aquatic toxicity classification by Verhaar (Modified)
Domain
logical expression index: "e"
Referential
boundary: The
target chemical should be classified as Acid moiety AND Phenols by
Aquatic toxicity classification by ECOSAR
Domain
logical expression index: "f"
Referential
boundary: The
target chemical should be classified as No alert found by DNA binding by
OECD
Domain
logical expression index: "g"
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 >> Alkyl phenols OR Michael addition >> P450
Mediated Activation to Quinones and Quinone-type Chemicals >> Arenes OR
Michael addition >> P450 Mediated Activation to Quinones and
Quinone-type Chemicals >> Hydroquinones 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 >> Aromatic nitro OR SN1
>> Nitrenium Ion formation >> Primary aromatic amine OR SN1 >> Nitrenium
Ion formation >> Tertiary aromatic amine by DNA binding by OECD
Domain
logical expression index: "h"
Referential
boundary: The
target chemical should be classified as No alert found by Protein
binding by OECD
Domain
logical expression index: "i"
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 SNAr OR SNAr >> Nucleophilic
aromatic substitution OR SNAr >> Nucleophilic aromatic substitution >>
Halo-triazines by Protein binding by OECD
Domain
logical expression index: "j"
Referential
boundary: The
target chemical should be classified as Bioavailable by Lipinski Rule
Oasis ONLY
Domain
logical expression index: "k"
Referential
boundary: The
target chemical should be classified as No alert found by
Carcinogenicity (genotox and nongenotox) alerts by ISS
Domain
logical expression index: "l"
Referential
boundary: The
target chemical should be classified as o-phenylphenol (Nongenotox) OR
Phtalate (or buthyl) diesters and monoesters (Nongenotox) OR Structural
alert for nongenotoxic carcinogenicity by Carcinogenicity (genotox and
nongenotox) alerts by ISS
Domain
logical expression index: "m"
Referential
boundary: The
target chemical should be classified as Known precedent reproductive and
developmental toxic potential AND Toluene and small alkyl toluene
derivatives (8a) by DART scheme v.1.0
Domain
logical expression index: "n"
Referential
boundary: The
target chemical should be classified as Not known precedent reproductive
and developmental toxic potential by DART scheme v.1.0
Domain
logical expression index: "o"
Referential
boundary: The
target chemical should be classified as Group 14 - Carbon C AND Group 16
- Oxygen O by Chemical elements
Domain
logical expression index: "p"
Referential
boundary: The
target chemical should be classified as Group 16 - Sulfur S by Chemical
elements
Domain
logical expression index: "q"
Parametric
boundary:The
target chemical should have a value of log Kow which is >= 1.64
Domain
logical expression index: "r"
Parametric
boundary:The
target chemical should have a value of log Kow which is <= 3.42
Description of key information
Toxicity to aquatic algae and cynobacteria:
Based on the prediction done using the OECD QSAR toolbox version 3.4 with log kow as the primary descriptor and considering the five closest read across substances, toxicity on Desmodesmus subspicatus (previous name: Scenedesmus subspicatus)was predicted for2-hydroxy-p-toluic acid (m cresotic acid) (50-85-1).The EC50 value was estimated to be 112.814 mg/l when 2-hydroxy-p-toluic acid (m cresotic acid)exposed toDesmodesmus subspicatus for 72 hrs.
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 112.814 mg/L
Additional information
Toxicity to aquatic algae and cynobacteria:
Based on the prediction done using the OECD QSAR toolbox version 3.4 with log kow as the primary descriptor and considering the five closest read across substances, toxicity on Desmodesmus subspicatus (previous name: Scenedesmus subspicatus)was predicted for 2-hydroxy-p-toluic acid (m cresotic acid) (50-85-1).The EC50 value was estimated to be 112.814 mg/l when 2-hydroxy-p-toluic acid (m cresotic acid)exposed toDesmodesmus subspicatus for 72 hrs.
The above prediction was supported another prediction for the target .Based on the prediction done using thethree different models i.e, Battery, Leadscope and SciQSAR used within Danish QSAR database, the short term toxicity on green algae was predicted for test substance m cresotic acid (2 -hydroxy-p-toluic acid) for cas 50 -85 -1. The average EC50 value was given by the third model i.e, Battery model. On the basis of effects observed in a static freshwater system, the effect concentration EC50 value for the substance m cresotic acid is estimated to be 159.23 mg/l for Pseudokirchneriella subcapitata during 72 hr exposure duration. Thus, on the basis of EC50 value,it can be concluded that the test chemical m cresotic acid can be considered as non toxic to green algae at environmentally relevant concentrations and can be considered not classified as per the CLP classification criteria.
The above predictions were further supported by summarized in Japan chemicals collaborative knowledge database (J-check), 2016 for structurally similar read across substance 4-Hydroxybenzoic acid (CAS: 99 -96 -7).
Short term toxicity toalgaestudy was carried out for 72 hrs. The study was performed according toOECD guideline 201 (Algal, Growth Inhibition Test).The study was based on the effects of the test compound onalgaein a static fresh water system.Based on effect on growth rate ofalgae,the 72 hr EC50 and NOEC value was determined to be 110 and 51 mg/l, respectively, and on the basis of AUG, the 72 hr EC50 and NOEC value was determined to be 69 and 32 mg/l, respectively.Thus, based onEC50value (110 mg/l), it can be concluded that the substance4-Hydroxybenzoic acidcan be considered as non-toxic to aquatic organisms and thus cannot be classifiedas hazardous, as per the CLP criteria.
The above experimental data was further supported by Ecotox database, U.S Environmental Protection Agency,2017 for structurally similar read across substance Salicylic acid (CAS: 69 -72 -7).
Short term toxicity study to Haematococcus pluvialis by using chemical salicylic acid was carried out, by using static method. Based on the growth inhibition of population of Haematococcus pluvialis, EC10 was 165 mg/l.Hence chemical salicylic acid was consider non toxic and can be concluded as not classified as per the CLP classification criteria.
Another experimental study for the structurally similar read across substance Benzoic acid (CAS: 65 -85 -0) was sumarized inECOTOX database, U. S. Environmental Protection Agency, 2016
Short term toxicity toPseudokirchneriella subcapitata(green algae) study was carried out for 48 hrs.The study was based on the effects of the test compound Benzoic acid (CAS: 65 -85 -0) onPseudokirchneriella subcapitatain a static fresh water system. On the basis of population of the test organismPseudokirchneriella subcapitata(green algae), the 48 hr EC50 value was determined to be 207.5 mg/l.
Thus, based on this values of target as well as structurally similar read across substance , it can be concluded that the substance 2-hydroxy-p-toluic acid (m cresotic acid) (50-85 -1) can be considered as non-toxic to aquatic organisms and thus cannot be classified as hazardous as per the CLP criteria.
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