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EC number: 604-636-5 | CAS number: 148477-71-8
- 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
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Adsorption / desorption
Administrative data
Link to relevant study record(s)
- Endpoint:
- adsorption / desorption: screening
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 121 (Estimation of the Adsorption Coefficient (Koc) on Soil and on Sewage Sludge using High Performance Liquid Chromatography (HPLC))
- Version / remarks:
- draft
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- other: 95/36/EC
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of method:
- HPLC estimation method
- Media:
- soil
- Radiolabelling:
- no
- Test temperature:
- oven temperature: 40 °C
- Details on study design: HPLC method:
- HPLC is performed on analytical columns packed with a commercially available cyanopropyl solid phase containing lipophilic and polar moieties. While passing through the column along with the mobile phase the test substance interacts with the stationary phase. As a result of partitioning between mobile and stationary phases the test substance is retarded. The dual composition of the stationary phase having polar and non-polar sites allows for interaction of polar and non-polar groups of a molecule in a similar way as is the case for organic matter in soil. This enables the relationship between the retention time on the column and the adsorption coefficient on organic matter to be established. This test is useful for chemicals, which are difficult to study in other experimental systems, i.e. a batch equilibrium test. The pH-value has a significant influence on sorption behaviour in particular for polar substances. For agricultural soils pH normally varies between pH 5.5 and 7.5.
- Analytical monitoring:
- yes
- Details on sampling:
- The objective of this study was to determine the mobility of Spirodiclofen in soil by estimation of the adsorption coefficient. In the present study the adsorption coefficient K0c of Spirodiclofen was investigated using High-Performance Liquid Chromatography (HPLC). The retention time of the test substance measured in this study was used to calculate Koc -values for Spirodiclofen.
- Details on test conditions:
- TEST CONDITIONS
- Buffer:Citric acid monohydrate, Merck, No. 1.00244.1000 adjusted to pH 6.0 with a water based solution of Sodium Hydroxide, Merck, No. 6498.1000
- methanol: Promochem, No. 3041 D-46485 Wesel
- Water: cleaned in a Milli-Q unit
Test System:
In the OECD proposal for a new guideline "Estimation of the Adsorption Coefficient (Koc) on Soil using HPLC" [2] the test is required to be carried out using a liquid chromatograph, fitted with a pulse-free pump and a suitable detection device. Commercial cyanopropyl chemically bound resins on a silica base was used. As mobile phase methanol/0.01 M citrate-buffer pH 6.0 (55/45, v/v) was used
Stock solution of the reference substances
An amount of approx. 10 mg of the reference substances was weighed into a 10-mL volumetric flask and diluted to volume with methanol.
Standard solutions:
According to the guideline, the maximum concentration of the test substance should not exceed 1/2 the solubility in the solvent. Therefore the measurements were carried out at concentrations of approx. 5 mg/L. The solvent was similar to the mobile phase of the HPLC method (i.e. methanol / citrate buffer pH 6.0, 55/45, v/v). A total of 0.1 ml_ taken from the standard stock solution was transferred into a 20-mL volumetric flask and diluted to volume with the mobile phase methanol / citrate buffer pH 6.0. The flask was shaken and ultrasonicated for one minute to dissolve the substance. - Key result
- Sample No.:
- #1
- Type:
- Koc
- Value:
- 31 037
- pH:
- 6
- Matrix:
- (methanol / citrate buffer pH 6.0, 55/45, v/v)
- Details on results (HPLC method):
- HPLC retention time data for the reference compounds are given in Table 1. The dead time (to) was determined to be 1.536 minutes using sodium nitrate. Variability of the retention times from repetitive injections was low, confirming HPLC system stability throughout the analysis period. Representative chromatograms are given in Appendix 2 to Appendix 15. The HPLC solvent blank injections showed a small undisturbing contamination at 2.84 minutes retention time throughout the analyses. The KOC value estimated for Spirodiclofen is 31,037.
- Validity criteria fulfilled:
- yes
- Executive summary:
The adsorption coefficient KOC of the test item on soil was estimated using High Performance Liquid Chromatography (HPLC).
Thirteen reference standards of known K0c were chromatographed on a HPLC system to determine an average capacity factor k'. Sodium nitrate was used to determine the HPLC system dead time (to). A regression line was plotted with the
determined k' values and the known KOC values (log k' vs. log K0c)- Spirodiclofen was chromatographed on the same HPLC system during the same sample sequence as the reference substances, and average k' values were determined. The KOC value for Spirodiclofen was estimated by interpolation from the reference substance regression line. The linear regression of measured k' values against literature K0c values yielded a line with a slope of 2.95, an intercept of 1.97 and a correlation coefficient R2 of 0.9076.
The estimated K0c value for Spirodiclofen is 31,037.
Reference
Description of key information
Key value for chemical safety assessment
- Koc at 20 °C:
- 31 037
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.
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