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EC number: - | CAS number: -
- 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
Adsorption / desorption
Administrative data
Link to relevant study record(s)
- Endpoint:
- adsorption / desorption: screening
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- Jun 2020 - May 2021
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 106 (Adsorption - Desorption Using a Batch Equilibrium Method)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of method:
- batch equilibrium method
- Media:
- soil
- Specific details on test material used for the study:
- 17-194T, Lot #: 300567-78-7
Composition: P,P-diethyl, monoester with 1,2 propanediol - 92.9%, CAS #2230512-72-6
Physical Description: Clear, transparent liquid
pH: Neutral to slightly acidic
Stability: Test substance was expected to be stable for the duration of testing.
Expiration Date: aug 30, 2022 - Radiolabelling:
- no
- Test temperature:
- 25 oC
- Analytical monitoring:
- yes
- Details on sampling:
- - Sampling interval: Samples of 0.3 mL were taken at 2, 4, 6, 21.5, 45.3, 68.5 and 141.9 hours for soil 1 and 2, not autoclaved as no equilibration was achieved. Samplings were performed for the auto-claved soils soils 3,4 and 5 at 2, 4, 6, 24 and 48 hours.
- Sample storage before analysis:no - Matrix no.:
- #1
- Matrix type:
- sandy loam
- % Clay:
- 8.9
- % Silt:
- 13.9
- % Sand:
- 77.2
- % Org. carbon:
- 2.12
- pH:
- >= 5.46
- CEC:
- 8.5 meq/100 g soil d.w.
- Bulk density (g/cm³):
- 1.232
- Matrix no.:
- #2
- Matrix type:
- clay
- % Clay:
- 41.2
- % Silt:
- 35.5
- % Sand:
- 23.3
- % Org. carbon:
- 1.46
- pH:
- 7.33
- CEC:
- 23.2 meq/100 g soil d.w.
- Bulk density (g/cm³):
- 1.299
- Matrix no.:
- #3
- Matrix type:
- silt loam
- % Clay:
- 23.9
- % Silt:
- 60.6
- % Sand:
- 15.5
- % Org. carbon:
- 5.04
- pH:
- 5.53
- CEC:
- 17.3 meq/100 g soil d.w.
- Matrix no.:
- #4
- Matrix type:
- clay
- % Clay:
- 75
- % Silt:
- 21.9
- % Sand:
- 3.3
- % Org. carbon:
- 3.08
- pH:
- 5.3
- CEC:
- 28.32 meq/100 g soil d.w.
- Matrix no.:
- #5
- Matrix type:
- loamy sand
- % Clay:
- 6
- % Silt:
- 12.6
- % Sand:
- 81.6
- % Org. carbon:
- 7.35
- pH:
- 2.98
- CEC:
- 6.12 meq/100 g soil d.w.
- Details on test conditions:
- Tier 1
In the preliminary test, the optimal soil/solution ratio was determined. The air-dried soil samples were shaken with 30 mL (blanks) resp. 27 mL of a 0.01 M CaCl2-solution over-night. 3 mL of test item stock solution (nominal concentration 5000 mg/L) was added to all 27 mL preparations to result in a test item solution with nominal concentration 100 mg/L. The following soils were used in tier 1: Refesol 03-G (S3) and Soil Eurosoil 5 (S5); with the ratios: 1.1 : 1; 1 : 1 and 0.7 : 1 for soil 3 resp. 1.2 : 1, 1 : 1 and 0.7 : 1 for soil 5.
One blank per soil and ratio with soil and CaCl2 solution (without test item) was prepared in order to determine the background signal.
Two adsorption control samples with the test item in CaCl2 solution (without soil) were included in order to check the stability of the test item in CaCl2 and the adsorption on the vessel surface.
The final volume of the aqueous phase was 30 mL for all ratios.
Tier 2
30 g of the air-dried soil samples were shaken with 30 mL resp. 27 mL of a 0.01 M CaCl2-solution overnight. 3 mL of test item stock solution (nominal concentration 5000 mg/L) was added to all 27 mL approaches to result in a test item solution with nominal concentration 500 mg/L.
Additionally, one blank per soil was prepared for the determination of the background signal, and two adsorption controls containing test item and CaCl2 solution were prepared for the determination of stability and adsorption on the vessel surface.
The final volume of the aqueous phase was 30 mL for all preparations. - Sample No.:
- #1
- Duration:
- 48 h
- Initial conc. measured:
- 500 other: mg/L
- pH:
- 6.09
- Temp.:
- >= 24.2 - <= 24.9 °C
- Remarks:
- Nominal concentrations t0 are reported
- Sample No.:
- #2
- Duration:
- 48 h
- Initial conc. measured:
- 500 other: mg/L
- pH:
- 7.36
- Temp.:
- >= 24.2 - <= 24.9 °C
- Remarks:
- Nominal concentrations t0 are reported
- Sample No.:
- #3
- Duration:
- 48 h
- Initial conc. measured:
- 500 other: mg/L
- pH:
- 5.85
- Temp.:
- >= 25 - <= 25.1 °C
- Remarks:
- Nominal concentrations t0 are reported
- Sample No.:
- #4
- Duration:
- 48 h
- Initial conc. measured:
- 500 other: mg/L
- pH:
- 5.44
- Temp.:
- >= 25 - <= 25.1 °C
- Remarks:
- Nominal concentrations t0 are reported
- Key result
- Sample No.:
- #1
- Type:
- Koc
- Value:
- 1.49 L/kg
- Key result
- Sample No.:
- #2
- Type:
- Koc
- Value:
- 5.92 L/kg
- Key result
- Sample No.:
- #3
- Type:
- Koc
- Value:
- 1.41 L/kg
- Key result
- Sample No.:
- #4
- Type:
- Koc
- Value:
- 8.79 L/kg
- Transformation products:
- not measured
- Remarks:
- Biodegradation is presented in the not autoclaved soils. the the soils wre autoclaved
- Validity criteria fulfilled:
- yes
- Conclusions:
- No values of Kd, multiplied with the soil-solution-ratio, resulted in a value of > 0.3 cm3/g (rounded values). Therefore, tier 3 was not determined. KOC was determined with 1.28 – 8.79 cm3/g.
Apparently, the adsorption behaviour of the test item is not strictly correlated with the or-ganic carbon content of the respective soil.
It is concluded, that only the soils with high clay content showed KOC values >2, whereby the adsorption is probably mainly caused by the clay content and not by the content of or-ganic carbon
Reference
Description of key information
Apparently, the adsorption behaviour of the test item is not strictly correlated with the organic carbon content of the respective soil.
The highest KOCvalue was obtained with Eurosoil 1 (clay content 75%), the next highest KOCvalue was obtained with soil Lufa 6S (clay content 41.2%). Soils with high content of clay can adsorb a higher content of humus, and clay-humus compexes occur. These complexes are able to adsorb polar organic substances.
It is concluded, that only the soils with high clay content showed KOCvalues >2, whereby the adsorption is probably mainly caused by the clay content and not by the content of organic carbonKey value for chemical safety assessment
- Koc at 20 °C:
- 5.29
Additional information
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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