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EC number: 203-453-4 | CAS number: 107-02-8
- 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
Other distribution data
Administrative data
- Endpoint:
- other distribution data
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: study documented in sufficient details
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 970
Materials and methods
- Principles of method if other than guideline:
- Acrolein was injected into an irrigation canal for a continuous period and the concentration of the test compound in the air above the water surface was measured using GC/UV.
- GLP compliance:
- no
- Type of study:
- volatility
- Media:
- water - air
Test material
- Reference substance name:
- Acrylaldehyde
- EC Number:
- 203-453-4
- EC Name:
- Acrylaldehyde
- Cas Number:
- 107-02-8
- Molecular formula:
- C3H4O
- IUPAC Name:
- acrylaldehyde
Constituent 1
Results and discussion
Any other information on results incl. tables
Acrolein (ca. 0.7 ppm) was injected into an irrigation canal (10 -11°C during the day, 6°C during the night; flow velocity: 1.7 ft/sec) for a continuous period (6 h, 20 min) and the concentration of the test compound in the air above the water surface was measured at four sites (1, 3, 6, and 9.5 miles below point of application) using GC/UV. For this, a small, steady stream of air was drawn for two hours through volatilimeters across an enclosed water surface of known area, and bubbled through a solution containing 2,4 -DNPH-hydrazine.
The following results were obtained:
Acrolein losses by volatilization from canal surfaces
Distance below injection point (mile(s)) |
Acrolein volatilised per surface mile of canal (mg/h) |
Percent of acrolein volatilised per mile |
1 mile |
27.0 mg/h |
0.31% |
3 mile |
20.7 mg/h |
0.35% |
6 mile |
15.2 mg/h |
0.17% |
9.5 mile |
11.5 mg/h |
0.13% |
Acrolein residual solution concentrations and calculated losses from point of application
Miles below injection point |
Acrolein concentration (ppm)* |
Acrolein loss per mile % |
Acrolein losses summation % |
1 |
0.710 |
1.4 |
1.4 |
3 |
0.691 |
1.3 |
4.0 |
6 |
0.590 |
4.7 |
18.1 |
9.5 |
0.404 |
7.4 |
43.9 |
12.5 |
0.361 |
2.0 |
49.9 |
16.0 |
0.340 |
0.8 |
52.8 |
19.0 |
0.329 |
0.5 |
54.3 |
22.5 |
0.319 |
0.4 |
55.7 |
27.0 |
0.269 |
1.5 |
62.6 |
*average of three samples taken 1, 3, and 5 h after acrolein front reached sampling station
Based on the results of water and air concentration measurements (only small losses due to volatilization), the authors concluded that reaction of acrolein with suspended or sedimented particulates might be of considerable importance.
Applicant's summary and conclusion
- Conclusions:
- Acrolein (ca. 0.7 ppm) was injected into an irrigation canal (10 -11°C during the day, 6°C during the night; flow velocity: 1.7 ft/sec) for a continuous period (6 h, 20 min) and the concentration of the test compound in the air above the water surface was measured at four sites (1, 3, 6, and 9.5 miles below point of application) using GC/UV. For this, a small, steady stream of air was drawn for two hours through volatilimeters across an enclosed water surface of known area, and bubbled through a solution containing 2,4 -DNPH-hydrazine. Based on the results of water and air concentration measurements (only small losses due to volatilization: 0.13-0.35% of applied acrolein), the authors concluded that reaction of acrolein with suspended or sedimented particulates might be of considerable importance.
- Executive summary:
Acrolein (ca. 0.7 ppm) was injected into an irrigation canal (10 -11°C during the day, 6°C during the night; flow velocity: 1.7 ft/sec) for a continuous period (6 h, 20 min) and the concentration of the test compound in the air above the water surface was measured at four sites (1, 3, 6, and 9.5 miles below point of application) using GC/UV. For this, a small, steady stream of air was drawn for two hours through volatilimeters across an enclosed water surface of known area, and bubbled through a solution containing 2,4 -DNPH-hydrazine.
The following results were obtained:
Acrolein losses by volatilization from canal surfaces
Distance below injection point (mile(s))
Acrolein volatilised per surface mile of canal (mg/h)
Percent of acrolein volatilised per mile
1
27.0
0.31
3
20.7
0.35
6
15.2
0.17
9.5
11.5
0.13
Acrolein residual solution concentrations and calculated losses from point of application
Miles below injection point
Acrolein concentration (ppm)*
Acrolein loss per mile %
Acrolein losses summation %
1
0.710
1.4
1.4
3
0.691
1.3
4.0
6
0.590
4.7
18.1
9.5
0.404
7.4
43.9
12.5
0.361
2.0
49.9
16.0
0.340
0.8
52.8
19.0
0.329
0.5
54.3
22.5
0.319
0.4
55.7
27.0
0.269
1.5
62.6
*average of three samples taken 1, 3, and 5 h after acrolein front reached sampling station
Based on the results of water and air concentration measurements (only small losses due to volatilization), the authors concluded that reaction of acrolein with suspended or sedimented particulates might be of considerable importance
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