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EC number: 214-122-9 | CAS number: 1087-21-4
- 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

Toxicity to microorganisms
Administrative data
Link to relevant study record(s)
- Endpoint:
- toxicity to microorganisms
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Justification for type of information:
- ANALOGUE APPROACH JUSTIFICATION
Please refer to attached docum - Principles of method if other than guideline:
- Assessment of inhibition of cell multiplication by the protozoon, Uronema parduzci. The number of protozoa was determined by means of a cell counter.
- GLP compliance:
- not specified
- Analytical monitoring:
- not specified
- Vehicle:
- not specified
- Test organisms (species):
- Uronema parduzci
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 20 h
- Test temperature:
- 25°C
- Details on test conditions:
- EFFECT PARAMETERS MEASURED
Number of protozoa by means of a cell counter
The protozoa cultures are fed with bacterial suspensions of Escherichia coli
EVALUATION
For mathematical evalutation of toxicological findings at the end of the test period, the mean value (A) of impulses/ml in test cultures free from toxic
influence or non-stimulated test cultures is calculated, provided the counts are within a standard deviation range of <5%. The mean value (B) of counts performed in test cultures of the lowest toxic pollutant concentration of the dilution series are also calculated.
As coordinates, (a) (highest non-toxic pollutant concentration) over (A) and (b) (lowest toxic pollutant concentration) over (B) are entered into a suitable electronic calculator. After having entered (A - 5%), the pollutant concentration at which inhibitory action begins (c) may be obtained from the regression line between (a;A) to (b;B). The findings obtained are given in the following paragraphs for pollutant concentrations at which the onset of inhibitory action was observed have been obtained by mathematical evaluation of counts. - Key result
- Duration:
- 20 h
- Dose descriptor:
- other: TGK
- Effect conc.:
- 22 mg/L
- Basis for effect:
- growth inhibition
- Validity criteria fulfilled:
- not specified
- Conclusions:
- Diallyl phthalate is not reported as toxic to the protozoan Uronema parduzci with a threshold concentration of 22 mg/l.
Reference
Description of key information
DAIP read-across from DAP - The key value is based on published studies
with four different species: Pseudomonas putida, Entosiphon sulcatum,
Uronema parduzci and Chilomonas paramecium. Although the separate
studies themselves are not sufficient enough to assess a key value for
the toxicity of diallyl phthalate in micro-organisms, the combination of
these four publications give a reliable value.
Key value for chemical safety assessment
- EC10 or NOEC for microorganisms:
- 22 mg/L
Additional information
Diallyl phthalate, a closely related structural analogue for DAIP, proved to be non-toxic for micro-organisms based on the results of various studies with four different species.
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