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EC number: 407-950-9 | CAS number: 895-85-2 INTEROX-PMBP-70W; INTEROX-PMPB-70W
- 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:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: The study was performed under GLP according to protocol. It was reviewed in the HPV program and recorded in the OECD SIDS dossier as reliability 1.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- GLP compliance:
- yes
- Analytical monitoring:
- yes
- Vehicle:
- no
- Test organisms (species):
- Daphnia magna
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Nominal and measured concentrations:
- Nominal: 3.0, 5.1, 8.7, 15 25, 43 and 72 mg/L
- Reference substance (positive control):
- not specified
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 42 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Conclusions:
- This study is reliable. It is performed according to OECD guideline 202 under GLP and it was reviewed during the HPV process. The calculated endpoints are adequate for C&L and risk assessment purposes.
- Executive summary:
For daphnids, Daphnia magna, an acute toxicity of p-toluic acid was 48 h EC50of 42 mg/L (MOE, 2003). A static test was conducted, twenty daphnids per test concentration were exposed at the concentrations of 3.0, 5.1, 8.7, 15 25, 43 and 72 mg/L nominal of the chemical together with a blank control group. The exposure concentrations were kept throughout the test period; the mean measured concentrations of p-toluic acid (geometric mean) of each treatment were 2.9, 4.8, 8.3, 14, 24, 41 and 70 mg/L, respectively, and the measured concentrations showed at the start and end of test were ranged 94.6 - 97 % of nominal and 95.3 - 98.2 % of nominal, respectively.The exposure was conducted without pH adjustment however pH was decreased to 4.9 at the highest concentration of 70 mg/L due to the test substance property. At the lower concentrations of the chemical pH was not changed significantly from that of dilution water. At the control and up to 14 mg/L (mean measured concentration) no immobilization was observed for 48 hr. At the highest concentration of 70 mg/L all daphnids were immobilized. Based on mean measured concentration the 48 h EC50 of 42 mg/L was calculated by using the probit analysis. At the concentration 41 mg/L (pH was 6.9 - 7.6) 8 of 20 individuals (40 %) of daphnids were immobilized, therefore the value of LC50 indicate a true toxicity of this chemical instead of a low pH effect, however at high concentrations a pH effect should be present. Then, the test is regarded as high reliability because no deviations from the OECD Test Guideline 202 occurred.
Reference
Description of key information
For daphnids, Daphnia magna, an acute toxicity of p-toluic acid was 48 h EC50of 42 mg/L (MOE, 2003). A static test was conducted, twenty daphnids per test concentration were exposed at the concentrations of 3.0, 5.1, 8.7, 15 25, 43 and 72 mg/L nominal of the chemical together with a blank control group. The exposure concentrations were kept throughout the test period; the mean measured concentrations ofp-toluic acid(geometric mean) of each treatment were 2.9, 4.8, 8.3, 14, 24, 41 and 70 mg/L, respectively, and the measured concentrations showed at the start and end of test were ranged 94.6 - 97 % of nominal and 95.3 - 98.2 % of nominal, respectively.The exposure was conducted without pH adjustment however pH was decreased to 4.9 at the highest concentration of 70 mg/L due to the test substance property. At the lower concentrations of the chemical pH was not changed significantly from that of dilution water.At the control and up to 14 mg/L (mean measured concentration) no immobilization was observed for 48 hr. At the highest concentration of 70 mg/L all daphnids were immobilized. Based on mean measured concentration the 48 h EC50 of 42 mg/L was calculated by using the probit analysis. At the concentration 41 mg/L (pH was 6.9 - 7.6) 8 of 20 individuals (40 %) of daphnids were immobilized, therefore the value of LC50 indicate a true toxicity of this chemical instead of a low pH effect, however at high concentrations a pH effect should be present.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 42 mg/L
Additional information
Due to rapid hydrolysis of 895-85-2 (see van Dam, 2014), the aquatic results of p-toluic acid are considered most relevant.
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