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EC number: 616-466-9 | CAS number: 77501-63-4
- 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
Other distribution data
Administrative data
- Endpoint:
- other distribution data
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1985
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Data from peer-reviewed handbook or collection of data; comparable to guideline study with acceptable restrictions
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 985
- Report date:
- 1985
Materials and methods
- Principles of method if other than guideline:
- The mobilities of (2-ethoxy-1-methyl-2-oxoethyl)-5-[2-chloro-4-(trifluoromethyl) phenoxy]-2-nitrobenzoate and its three major soil degradates, its initial hydrolysis product, lactyl-5-[2-chloro-4-(trifluoromethyl) phenoxy]-2-nitrobenzoate (aerobic), its second hydrolysis product, 5-[2-chloro-4-(trifluoromethyl)phenoxy]-2-nitrobenzoic acid (aerobic) and its reduction product, 5-[2-chloro-4-(trifluoromethyl) phenoxy]-2-amino benzoic acid (anaerobic), in soil were examined in relation to their potential to be leached by water using thin layer chromatography on 6 soils.
- GLP compliance:
- not specified
- Type of study:
- soil leaching
- Media:
- water - soil
Test material
- Reference substance name:
- (2-ethoxy-1-methyl-2-oxoethyl)-5-[2-chloro-4-(trifluoromethyl)phenoxy]-2-nitrobenzoate
- EC Number:
- 616-466-9
- Cas Number:
- 77501-63-4
- Molecular formula:
- C19H15ClF3NO7
- IUPAC Name:
- (2-ethoxy-1-methyl-2-oxoethyl)-5-[2-chloro-4-(trifluoromethyl)phenoxy]-2-nitrobenzoate
- Test material form:
- solid: particulate/powder
- Remarks:
- migrated information: particulates
- Details on test material:
- Radioactive Chemicals
14C-(2-Ethoxy-1-methyl-2-oxoethyl)-5-[2-chloro-4-(trifluoromethyl) phenoxy]-2-nitrobenzoate, uniformly labelled 14C in benzoic acid ring, 4 mCi/mmole, in acetone, 11.6 µg/µL, approximately 0.22 Mio. dpm/µL, for tests with Altvan, Hanford and Muscatine soils, > 98% purity.
14C-(2-Ethoxy-1-methyl-2-oxoethyl)-5-[2-chloro-4-(trifluoromethyl) phenoxy]-2-nitrobenzoate obtained from California Bionuclear, uniformly labelled 14c in benzoic acid ring, 195mCi/mmole, in methanol, 1.2 µg/µL, approximately 0.11 Mio. dpm/µL, for tests with Kibbie and Ritzsville soils, > 9S% C purity.
14C Atrazine from Pathfinder, uniformly labelled 14C ring labelled 58.3 mCi/mmole, in ethyl acetate, 1.3 µg/µL 1.1 x 10 dpm/µL, depending of type of experiment, purity of 83.5% increased by purification to 91.1%
5-[2-chloro-4-(trifluoromethyl)phenoxy]-2-nitrobenzoic acid California Bionuclear, 419 mCi/mmole in methanol, 0.685 mg/mL, 8.43 x 10 dpm/µl
lactyl-5-[2-chloro-4-(trifluoromethyl) phenoxy]-2-nitrobenzoate 19 mCi/mmole, uniformly labelled 14C in benzoic acid ring, in methanol, 1.12 mg/mL, 0.11 Mio. dpm/µL
5-[2-chloro-4-(trifluoromethyl) phenoxy]-2-amino benzoic acid, 14CF3 labelled, specific activity 7.20 mCi/mo1e, purified by TCC before use
Soils
(Characterization see below)
- Runford Series Soil
- Ritzsville Series Soil
- Altvan Series soil
- Wooster Series Soil
- Muscatine Series Soil
- Kibbie Series Soil
Constituent 1
Results and discussion
Any other information on results incl. tables
On all soils, 2-Ethoxy-1-methyl-2-oxoethyl)-5-[2-chloro-4-(trifluoromethyl) phenoxy]-2-nitrobenzoate was highly immobile with Rf values of almost 0. Rf values ranging from 0.13 to 0.91 for 5-[2-chloro-4-(trifluoromethyl) phenoxy]-2-nitrobenzoyl lactic acid, 0.31 to ca. 1 for 5-[2-chloro-4-(trifluoromethyl)phenoxy]-2-nitrobenzoic acid, and 0.08 to 0.62 for 5-[2-chloro-4-(trifluoromethyl) phenoxy]-2-amino benzoic acid, suggested that mobility of the degradates was significantly greater than the parental (2-Ethoxy-1-methyl-2-oxoethyl)-5-[2-chloro-4-(trifluoromethyl) phenoxy]-2-nitrobenzoate. Rfvalues correlated fairly to well with soil organic matter, ranging from 0.480 for 5-[2-chloro-4-(trifluoromethyl) phenoxy]-2-nitrobenzoyl lactic acid, to 0.878 for 5-[2-chloro-4-(trifluoromethyl) phenoxy]-2-amino benzoic acid.
Applicant's summary and conclusion
- Conclusions:
- 2-Ethoxy-1-methyl-2-oxoethyl)-5-[2-chloro-4-(trifluoromethyl) phenoxy]-2-nitrobenzoate is highly immobile in soil, whereas its degradation products, 5-[2-chloro-4-(trifluoromethyl) phenoxy]-2-nitrobenzoyl lactic acid (aerobic), 5-[2-chloro-4-(trifluoromethyl)phenoxy]-2-nitrobenzoic acid (aerobic) and 5-[2-chloro-4-(trifluoromethyl) phenoxy]-2-amino benzoic acid are more mobile, the mobility increasing with polarity.
- Executive summary:
The mobility of (2-ethoxy-1-methyl-2-oxoethyl)-5-[2-chloro-4-(trifluoromethyl) phenoxy]-2-nitrobenzoate and its three major soil degradates, its initial hydrolysis product, 5-[2-chloro-4-(trifluoromethyl) phenoxy]-2-nitrobenzoyl lactic acid (aerobic), its second hydrolysis product, 5-[2-chloro-4-(trifluoromethyl)phenoxy]-2-nitrobenzoic acid (aerobic) and its reduction product, 5-[2-chloro-4-(trifluoromethyl) phenoxy]-2-amino benzoic acid (anaerobic) in soil was examined in relation to its potential to be leached by water.
Thin layer chromatography was performed using six soils from different geographical locations, with an organic matter content between 0.43 and 2.6% w/w of the soil, as the stationary phase. On all soils, (2 -ethoxy-1-methyl-2-oxoethyl)-5-[2-chloro-4-(trifluoromethyl) phenoxy]-2-nitrobenzoate was highly immobile with Rf values of almost 0. Rf values ranging from 0.13 to 0.91 for 5-[2-chloro-4-(trifluoromethyl) phenoxy]-2-nitrobenzoyl lactic acid, 0.31 to ca. 1 for 5-[2-chloro-4-(trifluoromethyl)phenoxy]-2-nitrobenzoic acid, and 0.08 to 0.62 for 5-[2-chloro-4-(trifluoromethyl) phenoxy]-2-amino benzoic acid, suggested that mobility of the degradates was greater than that of the parental (2-ethoxy-1-methyl-2-oxoethyl)-5-[2-chloro-4-(trifluoromethyl) phenoxy]-2-nitrobenzoate in the soil/water system. Rf values correlated fairly to well with soil organic matter, ranging from 0.480 for 5-[2-chloro-4-(trifluoromethyl) phenoxy]-2-nitrobenzoyl lactate, to 0.878 for 5-[2-chloro-4-(trifluoromethyl) phenoxy]-2-amino benzoic acid, the anaerobic degradation product. The order of mobility was 5-[2-chloro-4-(trifluoromethyl) phenoxy]-2-nitrobenzoic acid > 5-[2-chloro-4-(trifluoromethyl) phenoxy]-2-amino benzoic acid > 5-[2-chloro-4-(trifluoromethyl) phenoxy]-2-nitrobenzoyl lactic acid > (2-Ethoxy-1-methyl-2-oxoethyl)-5-[2-chloro-4-(trifluoromethyl) phenoxy]-2-nitrobenzoate, with the parental substance being the less mobile of the tested substances.
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