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EC number: 820-225-5 | CAS number: 101747-77-7
- 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)
Description of key information
A study with the source substance Zinc bis[O,O-bis(2-ethylhexyl)] bis(dithiophosphate) (CAS 4259 -15 -8) was performed to assess the effect of the test material on the growth of the green alga Scenedesmus subspicatus. The method followed that described in the OECD Guidelines for Testing of Chemicals (1984) No. 201, “Alga Growth Inhibition Test” and was performed under GLP conditions. The quality of the study was assessed with Klimisch 2. Exposure of Scenedesmus subspicatus to the test material gave an EbL50 (72h) (based on biomass) value of 240 mg/L loading rate WAF and an ErL50 (72hr) (based on growth rate) value of 410 mg/L loading rate WAF. The No Observed Effect Loading rate was 220 mg/L loading rate WAF.
A study with the source substance Phosphorodithioic acid, mixed O,O-bis(1,3 -diemtylbutyl and iso Pr) esters, zinc salts (CAS 84605 -29 -8) was performed to assess the effect of the test material on the growth of the green alga Scenedesmus subspicatus. The method followed that described in the OECD Guidelines for Testing of Chemicals (1984) No. 201, “Alga Growth Inhibition Test” and was performed under GLP conditions.The quality of the study was assessed with Klimisch 2. Exposure of Scenedesmus subspicatus to the test material gave an EbL50 (72h) (based on biomass) value of 21 mg/L loading rate WAF and an ErL50 (72hr) (based on growth rate) value of 24 mg/L loading rate WAF. The No Observed Effect Loading rate was 10 mg/L loading rate WAF.
The values are different from each other. But this is in range with the category approach, where nevertheless the members of the categories may have different values.
For the CSA the lower value is chosen as worst-case value.
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 24 mg/L
- EC10 or NOEC for freshwater algae:
- 10 mg/L
Additional information
Zinc bis[O,O-bis(2-ethylhexyl)] bis(dithiophosphate) (CAS 4259 -15 -8)
Introduction:
A study was performed to assess the effect of the source substance Zinc bis[O,O-bis(2-ethylhexyl)] bis(dithiophosphate) (CAS 4259 -15 -8) on the growth of the green alga Scenedesmus subspicatus. The method followed that described in the OECD Guidelines for Testing of Chemicals (1984) No. 201, “Alga Growth Inhibition Test”.
Methods:
Following a preliminary range finding test, the alga were exposed to Water Accommodated Fractions of test material over a range of nominal loading rates of 10, 32, 220, 320, and 1,000 mg/L (three replicate flasks per concentration) for 72 hours, under constant illumination and shaking at a temperature of 24 degrees C. Samples of the algal populations were removed daily and cell concentrations determined for each control and treatment group using a Coulter Multisizer Particle Counter.
Results:
Exposure of Scenedesmus subspicatus to the test material gave an EbL50 (72h) value of 240 mg/L loading rate WAF and an ErL50 (0-72 hr) value of 410 mg/L loading rate WAF. The No Observed Effect Loading rate was 220 mg/L loading rate WAF.
Phosphorodithioic acid, mixed O,O-bis(1,3 -diemtylbutyl and iso Pr) esters, zinc salts (CAS 84605 -29 -8)
Introduction:
A study was performed to assess the effect of the test material on the growth of the green alga Scenedesmus subspicatus. The method followed that described in the OECD Guidelines for Testing of Chemicals (1984) No. 201, “Alga Growth Inhibition Test”.
Methods:
Following a preliminary range finding test, the alga were exposed to Water Accommodated Fractions of test material over a range of nominal loading rates of 10, 20, 40, 80, and 160 mg/L (three replicate flasks per concentration) for 72 hours, under constant illumination and shaking at a temperature of 24 °C. Samples of the algal populations were removed daily and cell concentrations determined for each control and treatment group using a Coulter Multisizer Particle Counter.
Results:
Exposure of Scenedesmus subspicatus to the test material gave an EbL50 (72h) (based on biomass) value of 21 mg/L loading rate WAF and an ErL50 (72hr) (based on growth rate) value of 24 mg/L loading rate WAF. The No Observed Effect Loading rate was 10 mg/L loading rate WAF.
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