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EC number: 248-383-5 | CAS number: 27277-00-5
- 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
Phototransformation in water
Administrative data
Link to relevant study record(s)
- Endpoint:
- phototransformation in water
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Non-GLP, available as unpublished report, minor restrictions in design and/or reporting but otherwise adequate for assessment
- Study type:
- direct photolysis
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- The stability of low (5ppm) and high (500ppm) concentration solutions of the test substance in water, in a dilute solution of ‘Gramoxone’ in water and in a dilute solution of acetone in water; exposed to sunlight at prevailing ambient temperatures was investigated.
- GLP compliance:
- no
- Radiolabelling:
- yes
- Analytical method:
- other: Chromatography was carried out on precoated 0.25mm layers of silica gel and Quantitative measurements were performed with radioscans of radioactive areas on chromatograms
- Details on sampling:
- Sub-samples of the solution (15mL) were withdrawn at 0, 1, 2, 4, 7, 14, and 27 days after the addition of the radioactivity. The subsamples were stored at -15°C until required for analysis.
- Light source:
- sunlight
- Details on light source:
- Weather conditions: This experiment was conducted between 22/5/76 and 6/8/76 in the open air. The general conditions were very hot with a great deal of direct sunlight.
- Details on test conditions:
- STOCK SOLUTION:
A stock solution was prepared containing 48.5 µCi of the C14-radioactive labeled test substance (1.41 mCi/mM) in 10 mL of methanol (i.e. 7.14 mg of substance in 10 mL).
TEST SOLUTIONS:
Portions of distilled water, a 1% solution of ‘Gramoxome U.K.’ in water and a 4% solution of acetone in water (250mL) were each treated with 1.75 mL of the labelled test substance solution to give 5 ppm solutions. The 500 ppm solution of the test substance was made with unlabelled test substance (120.7 mg) in methanol (5mL) in a 4% solution of acetone in water. he solutions were placed in 15cm crystallizing dishes and covered with polythene. The dishes were placed outside and exposed to sunlight from 22/5/1976 for up to 77 days.
As a control experiment 10µCi of 14C-diquat (compound II) of specific activity 29mCi/mM was dissolved in water with dry diquat dibromide (2.26 mg) to give the 5 ppm diquat ion solution.
The following solutions were used:
- Solution 1: 5ppm solution of labelled 14C-test substance in distilled water
- Solution 2: 5 ppm solution of labelled 14C-test substance in 1% ‘Gramoxone U.K. formulation’ in water
- Solution 3: 5ppm solution of labelled 14C-test substance in a 4% acetone-water solution.
- Solution 4: 500 ppm solution of unlabelled test substance in a 4% acetone water solution*
- Solution 5: 5 ppm 14C-diquat solution in water.
*Solution 4 provided a source of larger quantities of the degradation products. It has not been fully analyzed.
WEATHER CONDITIONS:
The general conditions were very hot with a great deal of direct sunlight. - Reference substance:
- yes
- DT50:
- ca. 4 d
- Transformation products:
- yes
- Details on results:
- ANALYSIS OF SOLUTIONS:
See 'Any other information on results incl. tables:
Although the results are variable, solutions 2 and 3 show the same trend of increases as the diquat solution; this may well be explained by concentration of the solution by evaporation during the experiment. The increase is of a similar order to that obtained with the diquat solution. The autoradiograms of the chromatograms of the aqueous solutions showed a rapid and comprehensive breakdown of the test substance, consequently a more intensive examination of the solution was undertaken.
ION-EXCLUSION CHROMATOGRAPHY OF THE SOLUTIONS:
See 'Any other information on results incl. tables:
The solutions were chromatographed on Amberlite XAD-2 resin. Autoradiograms of these chromatograms of the methanol eluates shows that the pattern of breakdown for each solution differs. For solution 2, the difference may be due to the presence of the coloured ‘Gramoxone’ and acetone could act as a photosensitizer in solution 3. However, the rate of photo degradation appeared to differ little between the solutions. In solution 1 and 3, compound 5 is the major product but in solution 2, compound 6 appears to be the major product. This compound is unusual in that it is less polar than the test substance. There are numerous minor degradation products more polar than the parent in all the solutions. - Results with reference substance:
- The 14C-diquat solution was sampled and analyzed as described. An autoradiogram of the samples reveals that the photo degradation proceeded smoothly throughout the period of the experiment. This suggests that no unexpected variables affected the photo degradation of the test substance solutions during the course of this study.
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The results show that aqueous solutions of the test substance are readily photodegradable in bright sunlight. The rate of degradation was rapid with half life of approximately 4 days. In the presence of ‘Gramoxone’ the degradation pattern changed but the rate of decay of the test substance was unchanged.
- Executive summary:
The stability of low (5ppm) and high (500ppm) concentration solutions of the test substance in water, in a dilute solution of ‘Gramoxone’ in water and in a dilute solution of acetone in water; exposed to sunlight at prevailing ambient temperatures was investigated. The following solutions were used to determine the photodegradability: solution1: 5ppm solution of labelled 14C-test substance in distilled water, solution 2: 5 ppm solution of labelled 14C-test substance in 1% ‘Gramoxone U.K. formulation’ in water,solution 3: 5ppm solution of labelled 14C-test substance in a 4% acetone-water solution, solution 4: 500 ppm solution of unlabelled test substance in a 4% acetone water solution, and solution 5: 5 ppm 14C-diquat solution in water. The results show that aqueous solutions of the test substance are readily photodegradable in bright sunlight. The rate of degradation was rapid with half life of approximately 4 days. In the presence of ‘Gramoxone’ the degradation pattern changed but the rate of decay of the test substance was unchanged.
Reference
The radioactivity in test substance solutions expressed as a percentage of the calculated added activity (7.53E+04 dpm/mL):
solution |
Percentage of added radioactivity at times (in days) |
||||||
|
0 |
1 |
2 |
4 |
7 |
14 |
27 |
5ppm solution of labelled 14C-test substance in distilled water |
102 |
96 |
92 |
87 |
86 |
96 |
89 |
5 ppm solution of labelled 14C-test substance in 1% ‘Gramoxone U.K. formulation’ in water |
* |
86 |
94 |
87 |
95 |
109 |
115 |
5ppm solution of labelled 14C-test substance in a 4% acetone-water solution |
95 |
94 |
99 |
107 |
117 |
124 |
No sample |
*spurious result
The percentage of radioactivity obtained in fractions from the XAD-2 chromatography of the C14 labelled test substance photodegradation solutions.
Solution |
1 |
1 |
1 |
1 |
1 |
2 |
2 |
2 |
2 |
2 |
2 |
3 |
3 |
3 |
3 |
3 |
3 |
day |
0 |
2 |
7 |
14 |
27 |
0 |
1 |
4 |
7 |
14 |
27 |
0 |
1 |
2 |
4 |
7 |
14 |
% in aqueous portion |
0 |
7 |
9 |
8 |
8 |
0 |
0 |
4 |
7 |
6 |
16 |
0 |
1 |
3 |
4 |
6 |
11 |
% in methanol soln 1* |
100 |
90 |
87 |
85 |
75 |
100 |
100 |
96 |
90 |
92 |
81 |
100 |
99 |
95 |
95 |
92 |
88 |
% in methanol Soln 2 onwards |
0 |
4 |
4 |
7 |
17 |
0 |
0 |
0 |
3 |
2 |
3 |
0 |
0 |
2 |
2 |
2 |
2 |
Approx. percentage of original activity recovered |
91 |
81 |
81 |
82 |
102 |
100 |
100 |
89 |
76 |
81 |
68 |
113 |
102 |
95 |
93 |
88 |
93 |
* Solutions labelled ‘Methanol solution1’ were concentrated in vacuo and chromatographed; these fractions contained an average of ca. 75% of the original radioactivity applied to the column.
Description of key information
The rate of degradation was rapid with half life of approximately 4 days.
Key value for chemical safety assessment
- Half-life in water:
- 4 d
Additional information
The stability of low (5ppm) and high (500ppm) concentration solutions of the test substance in water, in a dilute solution of ‘Gramoxone’ in water and in a dilute solution of acetone in water; exposed to sunlight at prevailing ambient temperatures was investigated. The following solutions were used to determine the photodegradability: solution1: 5ppm solution of labelled 14C-test substance in distilled water, solution 2: 5 ppm solution of labelled 14C-test substance in 1% ‘Gramoxone U.K. formulation’ in water, solution 3: 5ppm solution of labelled 14C-test substance in a 4% acetone-water solution, solution 4: 500 ppm solution of unlabelled test substance in a 4% acetone water solution, and solution 5: 5 ppm 14C-diquat solution in water. The results show that aqueous solutions of the test substance are readily photodegradable in bright sunlight. The rate of degradation was rapid with half-life of approximately 4 days. In the presence of ‘Gramoxone’ the degradation pattern changed but the rate of decay of the test substance was unchanged.
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