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EC number: 201-377-6 | CAS number: 81-81-2
- 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

Biodegradation in soil
Administrative data
- Endpoint:
- biodegradation in soil
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 991
- Report date:
- 1991
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- other: - Guideline IV, 4-1 of the Biologische Bundesanstalt (BBA), Braunschweig (FRG)
- GLP compliance:
- not specified
- Test type:
- laboratory
Test material
- Reference substance name:
- Warfarin
- EC Number:
- 201-377-6
- EC Name:
- Warfarin
- Cas Number:
- 81-81-2
- Molecular formula:
- C19H16O4
- IUPAC Name:
- 4-hydroxy-3-(3-oxo-1-phenylbutyl)-2H-chromen-2-one
- Details on test material:
- R,S-[benzene ring-U-14C] WARFARIN
Radiochemical purity by analytical HPLC : 96.5%
Total activity : 80 MBq, 2.16mCi
Specific activity : 470 MBq/mmol, 12.7mCi/mmol
(determined by gravimetric analysis) : 1.53 MBq/mg, 41 µCi/mg
Molecular weight : 308 (at this specific activity)
Constituent 1
- Radiolabelling:
- yes
Study design
- Soil classification:
- not specified
- Details on soil characteristics:
- Soil: Marsh Soil (Kalkmansch, silt loam)
Origin: Finkhaushalligkoog, southwest of Husum (FRG), close to the North Sea cost.
Vegetation: pasture, sheep grazing
Soil Analysis (Lufa Speyer)
Particle Size Distribution
Size Range in mm [%]
<0.002 mm [16]
0.002 to 0.006 mm [3.6]
0.006 to 0.020 mm [6.6]
0.020 to 0.063 mm [59.7]
0.063 to 0.200 mm [12.5]
0.200 to 0.630 mm [1.4]
0.630 to 2.000 mm [0.2]
Content of Organic Carbon: 1.8%
pH (CaCl2): 6.5
max. Water Capacity: 51.6%
Microbial Biomass (determined by LUPA Augustenburg): mg C/100g soil (dry weight)
start of the experiment: 50%
end of the experiment: 28%
Duration of test (contact time)
- Soil No.:
- #1
- Duration:
- 134 d
Initial test substance concentration
- Soil No.:
- #1
- Initial conc.:
- 550 mg/kg soil d.w.
- Based on:
- test mat.
- Parameter followed for biodegradation estimation:
- radiochem. meas.
Experimental conditions
- Soil No.:
- #1
- Temp.:
- 20 ± 2 ºC
- Humidity:
- 90%
- Details on experimental conditions:
- Soil Preparation: 15 Erlenmeyer flasks were prepared each containing 50 g (dry weight) soil, being adjusted to 40% of the maximum water capacity. The flasks were allowed to equilibrate for 2 weeks at 20 ± 2 ºC in the dark before the test substance was applied.
Unlabeled Warfarin and [14C]-Warfarin were dissolved in acetone, resulting in a concentration of [14C]-Warfarin at 26.1 mg/ml or 33 mg/g of solution. To 14 flasks an exactly weighed amount of ca. 0.8 g of the [14C]-Warfarin solution was added by pipette corresponding to a rate of 27 mg [14C]-Warfarin per 50 g (dry) soil or 550 mg/kg.
After application of the test substance each flask was equipped with a trap for volatile compounds including carbon dioxide. The trap consisted of a glass tube filled with paraffin oil impregnated quartz wool and soda lime. The flasks were stored in the dark at 20 ± 2 ºC and 90% relative humidity until analysis. The loss in water was checked by weighing from time to time and replaced by distilled water as appropriate.
Sampling occurred at days 0, 1.8, 6.7, 22, 52, 84, and 134. At each sampling, the volatile compounds were driven from the headspace of the flask into the trap by a stream of air. The soil was extracted with ultrasonication at room temperature for 10 min each with acetone (3 times) followed by soxhlett extraction with methanol for 12 h. The radioactivity in the different extract solutions was determined via LSC. The extract solutions were concentrated using rotary evaporation and analyzed by radio-LSC. After drying, the radioactivity retained in the soil samples was determined by means of combustion/LSC.
Analysis of the traps: Traps were extracted with ethyl acetate. For determination of the amounts of 14C-labelled carbonate, the soda lime was suspended in aqueous HCl (pH 1) in a closed system and during stirring and heating (70 ºC) a slight stream of nitrogen was driven over this solution and passed through an absorption liquid for carbon dioxide. The radioactivity in this solution was determined.
Radioactivity was measured in all liquid samples, in the combusted dried soil samples and for all samples analyzed by TLC.
Methylation of Warfarin for Comparative Analysis of Metabolites. Two experiments were run to obtain reference materials.
1. Methanol. Warfarin was refluxed with methanol and some hydrochloric acid for 15 hours. The solution was analyzed using the TLC method.
2. Diazomethane. Warfarin, dissolved in diethyl ether was treated with an etheral solution of diazomethane at room temperature. After evaporation of the solvent in a stream of nitrogen the residue was redissolved in methanol for TLC investigation.
Results and discussion
% Degradation
- Soil No.:
- #1
- % Degr.:
- 53.6
- Parameter:
- radiochem. meas.
- Sampling time:
- 134 d
Half-life / dissipation time of parent compound
- Soil No.:
- #1
- DT50:
- 150 d
- Type:
- (pseudo-)first order (= half-life)
- Transformation products:
- yes
Identity of transformation productsopen allclose all
- No.:
- #1
Reference
- Reference substance name:
- Unnamed
- IUPAC name:
- dioxomethane
- Inventory number:
- InventoryMultipleMappingImpl [inventoryEntryValue=EC 204-696-9]
- CAS number:
- 124-38-9
- Identity:
- Carbon dioxide
- Molecular formula:
- CO2
- Molecular weight:
- 44.01
- SMILES notation:
- O=C=O
- InChl:
- InChI=1/CO2/c2-1-3
- No.:
- #2
Reference
- Reference substance name:
- Unnamed
- IUPAC name:
- hexahydro-coumarin
- Identifier:
- common name
- Identity:
- hexahydro-coumarin
- No.:
- #3
Reference
- Reference substance name:
- Unnamed
- IUPAC name:
- 3-(alpha-hydroxy-benzyl)-4-hydroxycoumarin
- Identifier:
- common name
- Identity:
- 3-(alpha-hydroxy-benzyl)-4-hydroxycoumarin
- Evaporation of parent compound:
- yes
- Volatile metabolites:
- yes
- Residues:
- yes
- Details on results:
- The amount of radioactivity extractable from the soil in organic solvents (acetone and methanol) decreased during the study from 102% on day 0 to 64% on day 134, whereas the radioactivity retained in the soil increased to 14%. Within the same period, the amount of 14C-labelled carbon dioxide being the main metabolite increased to 16%.
The extractable radioactivity consisted mainly of parent compound, thus the amount of [14C]-Warfarin in the soil decreased from 98% at day 0 to 54% at day 134. From these data, it is concluded that the degradation of Warfarin follows a first order kinetics and a disappearance time DT50 of 150 days was calculated.
The main metabolite was found to be carbon dioxide which after 134 days storage of the soil comprised 16% of the radioactivity applied. Another 14% of the radioactivity were found to be retained in the soil after extraction with acetone and methanol.
Some minor amounts of radioactivity were found in three different peaks after separation of the extracted radioactivity using a TLC system with further purification by HPLC. The individual components were analysed by MS. A comparison is also made with experimentally derived metabolites from the methylation of unlabeled Warfarin. The report explains in detail the interpretation of the data leading to the identification and source of these minor transformation products.
Any other information on results incl. tables
Percent Degradation of [14C]-Warfarin in Soil
Sampling Day |
Extractable |
Residual |
Volatiles, CO2 |
Volatiles, other |
Σ (Balance) |
Warfarin |
0 |
101.9 |
0.4 |
- |
- |
102.3 |
98 |
1.8 |
100.6 |
1.1 |
0.1 |
<0.01 |
101.8 |
95.9 |
6.7 |
98.6 |
2.1 |
0.5 |
<0.01 |
101.2 |
93.9 |
22 |
93 |
4.5 |
4.1 |
<0.01 |
101.6 |
86 |
52 |
82.6 |
8.6 |
9.5 |
<0.01 |
100.7 |
77 |
84 |
75.8 |
10.1 |
11.9 |
<0.01 |
97.7 |
66.8 |
134 |
64.3 |
13.6 |
16.4 |
<0.01 |
94.3 |
53.6 |
Applicant's summary and conclusion
- Conclusions:
- The amount of [14C]-labeled test substance in the soil decreased from 98% at day 0 to 54% at day 134. From these data, it was concluded that the degradation of the test substance follows a first order kinetics and a disappearance time, DT50, of 150 days was calculated.
- Executive summary:
The degradation of [14C]-labeled test substance in soil was investigated at an application rate of 550 mg/kg using radio-analytical techniques and mass spectrometry. The disappearance time, DT50, was found to be approximately 150 days. The main metabolite was found to be carbon dioxide, after 134 days comprising 16% of the radioactivity applied. Furthermore, two minor metabolites were separated, comprising at most 5% each. From mass-spectrometric investigations, the following structures were derived: hexahydro-coumarin and 3-(alpha-hydroxy-benzyl)-4-hydroxycoumarin.
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