Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
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
Biotransformation and kinetics
Administrative data
- Endpoint:
- biotransformation and kinetics
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Basic data given, meets basic scientific principles
Data source
Reference
- Reference Type:
- publication
- Title:
- METABOLISM OF [14C]ACROLEIN (MAGNACIDE H® HERBICIDE): NATURE AND MAGNITUDE OF RESIDUES IN FRESHWATER FISH AND SHELLFISH
- Author:
- Nordone AJ, Dotson TA, Kovacs MF, Doane R, Biever RC
- Year:
- 1 998
- Bibliographic source:
- Environmental Toxicology and Chemistry, Vol. 17, No. 2, pp. 276-281
Materials and methods
Test guideline
- Qualifier:
- no guideline available
- Principles of method if other than guideline:
- assessment of metaboIism of acrolein and its residues in edible tissues of fish and shellfish
- GLP compliance:
- not specified
- Type of medium:
- aquatic
Test material
- Reference substance name:
- Acrolein
- IUPAC Name:
- Acrolein
- Details on test material:
- - Name of test material (as cited in study report): Acrolein
- Radiochemical purity (if radiolabelling): 92.2 %
- Specific activity (if radiolabelling): 648,980 dpm/µg
- Locations of the label (if radiolabelling): 2,3-14C-acrolein
Constituent 1
Results and discussion
- Transformation products:
- yes
Any other information on results incl. tables
Total
14-C and acrolein water concentration
The
estimated half-live of acrolein during the first 24 h was
L. macrochirus: 11.3 h
I. punctatus: 2.9 h.
Clam: 27.1 h
Crayfish: 27.8 h.
Total 14-C concentrations in tissue
L.
macrochirus:
The mean total 14-C residue concentrations (mg/kg as acrolein
equivalents) measured in the tissues of bluegill was 0.25 ± 0.05.
Recovery was 123% of the oxidized tissue values. The high recovery was
likely due to a combination of variability in compositing and initial
tissue processing procedure and in concentration of total 14-C residues
due to partial dehydration of tissue during storage.
I.
punctatus:
The mean total 14-C residue concentrations (mg/kg as acrolein
equivalents) measured in the tissues of catfish was0.22 ± .0.03.
Recovery was 151% of the oxidized tissue values. The high recovery was
likely due to a combination of variability in compositing and initial
tissue processing procedure and in concentration of total 14-C residues
due to partial dehydration of tissue during storage.
Crayfish:
The mean total 14-C residue concentrations (mg/kg as acrolein
equivalents) measured in the tissues of crayfish was 0.42 ± 0.02.
Recovery was 117% of the oxidized tissue values. The high recovery was
likely due to a combination of variability in compositing and initial
tissue processing procedure and in concentration of total 14-C residues
due to partial dehydration of tissue during storage.
Clam:
The mean total 14-C residue concentrations (mg/kg as acrolein
equivalents) measured in the tissues of clam was 5.34 ± 1.31. Recovery
was 127% of the oxidized tissue values. The high recovery was likely due
to a combination of variability in compositing and initial tissue
processing procedure and in concentration of total 14-C residues due to
partial dehydration of tissue during storage.
Metabolite identification and quantification
I.
punctatus:
Glycidol was the major acrolein metabolite found in the channel
catfish tissue, accounting for 54-57% of the total radioactive residue.
L. macrochirus:
The major acrolein metabolites found in the tissues of bluegill were
1,3-propanedio1 and glyceric acid, which accounted for 28 -40% and 14
-24%, respectively, of the tissue total radioactive residue.
Crayfish:
Glycerol and lactic acid were the major acrolein metabolites found in
the crayfish tissue, accounting for 45-61% and 11-19% of the tissue
total radioactive residue, respectively.
Clam:
Unidentified carbohydrates constituted the major 14C components in the
clam tissue, at 27-34% of the tissue total radioactive residue.
Table: Metabolite residues found in the tissues of test species (expressed as mg/kg acrolein equivalents)
Melabolite |
L. macrochirus |
I. punctatus |
Clam |
Crayfish |
Total water extractable [14C] residues |
0.22 |
0,17 |
4.7 |
0.35 |
Glycidol |
<0.01 |
0.12 |
0.05 |
0.02 |
Malonic acid |
0.02 |
0,03 |
-- |
0.07 |
Lactic acid |
-- |
0.03 |
0.48 |
0.05 |
Oxalic acid |
0.01 |
<0.01 |
-- |
0,01 |
1,3-Propanediol |
0.10 |
<0,01 |
0.11 |
-- |
Glycerol |
<0.01 |
<0.01 |
-- |
0.21 |
Glyceric acid |
0.04 |
-- |
1.18 |
-- |
Propiolic acid |
0.03 |
-- |
0.80 |
-- |
HCO3 |
0.01 |
-- |
-- |
-- |
Propanol |
-- |
-- |
0.05 |
-- |
Propionic acid |
-- |
-- |
0,37 |
-- |
Carbohydrates |
-- |
-- |
l,76 |
-- |
Unknowns |
-- |
-- |
0.05 |
0.01 |
Total NaOH extractable [14.C] residues |
0.02 |
0.04 |
0,64 |
0.06 |
Unknowns |
0.02 |
0.04 |
0.64 |
0.06 |
Neither
acrolein, acrylic acid, nor allyl alcohol were detected in the tissues
of any of the test species. Metabolites of acrolein found in the
water-extracted tissues were primarily alcohols and organic acids. These
results suggest that the rapid biodegradation of acrolein in aquaria
water is followed by the rapid and complete metabolism of the parent and
water-borne metabolites in the tissues of all four species tested.
Glyceric acid, propanol, oxalic acid, und propionic acid were the only
metabolites common to the fish, clam and crayfish tissue. These latter
four acrolein metabolites could have been either directly assimilated
from the test system or metabolic products produced by the test
organisms. All other acrolein metabolites identified in the fish, clam
and crayfish tissue, 1,3-propanediol, malonic acid, lactic acid,
propiolic acid, glycidol, and glycerol, were likely metabolic products
generated by the test species.
Conclusion:
Bluegill,
channel catfish, crayfish, and clams, when continuously exposed to
14C-acrolein and its residues are able to further metabolize these
compounds in their tissues to 10 identified metabolites, with a number
of polar and nonpolar compounds being generally characterized as
carbohydrates, amino acids, and peptides. The metabolism of 14C-acrolein
is so rapid in these species that neither acrolein nor its major
oxidative and reductive metabolites acrylic acid and allyl alcohol,
respectively, were detected in the tissues examined.
The results demonstrated that the potential of acrolein to enter and
persist in aquatic food chains is low.
Applicant's summary and conclusion
- Executive summary:
The fish species Lepomis macrochirus and Ictalurus punctatus, the clam Elliptio complanata and the crayfish Orconectes virilis were exposed to nominal concentration of 20.2 µg/L (fish) and 101µg/L (clam, crayfish) in static exposure test systems, with two applications of acrolein made at 7-d intervals. Exposure was terminated on day 8, 1 d after the second acrolein application. Test organisms were killed and their edible tissues were used for metabolite identification. Neither acrolein, acrylic acid, nor allyl alcohol were detected in the tissues of any of the test species. Metabolites of acrolein found in the water-extracted tissues were primarily alcohols and organic acids. These results suggest that the rapid biodegradation of acrolein in aquaria water is followed by the rapid and complete metabolism of the parent and water-borne metabolites in the tissues of all four species tested. They are able to further metabolize these compounds in their tissues to 10 identified metabolites, with a number of polar and nonpolar compounds being generally characterized as carbohydrates, amino acids, and peptides.
The results demonstrated that the potential of acrolein to enter and persist in aquatic food chains is low.
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.