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EC number: 849-290-8 | CAS number: 9001-97-2
- 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
Toxicity to aquatic algae and cyanobacteria
Administrative data
Link to relevant study record(s)
- Endpoint:
- toxicity to aquatic algae and cyanobacteria
- Type of information:
- read-across based on grouping of substances (category approach)
- Adequacy of study:
- key study
- Study period:
- August 1992 to November 1993
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Justification for type of information:
- The alpha amylase study was used as a key study for read-across given the sensitivity of this enzyme towards aquatic organisms.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Alga, Growth Inhibition Test)
- Deviations:
- no
- GLP compliance:
- yes
- Analytical monitoring:
- no
- Vehicle:
- no
- Details on test solutions:
- Method: The test substance was dissolved in sterile nutrient medium to give an initial stock solution of 200 mg/L. This stock solution was further diluted with sterile nutrient medium to produce a series of solutions exactly twice the concentration of the intended exposure levels. 150 mL of algal preculture was mixed with 150 mL of each of these solutions to give final test series.
- Controls: medium. - Test organisms (species):
- Desmodesmus subspicatus (previous name: Scenedesmus subspicatus)
- Details on test organisms:
- TEST ORGANISM
- Common name: green alga
- Strain: CCAP 276/20
- Source (laboratory, culture collection): Culture Centre of Algae & Protozoa c/o Freshwater Biological Association, Cumbria, UK
- Method of cultivation:
Pre-culture: Sterile nutrient medium was inoculated from a master culture and incubated under continuous illumination (ca. 7000 lux) and stirring (orbital shaker) at 24 ± 1°C to give an algal suspension in log phase growth.
Culture conditions: Conical flasks each containing 100 mL test or control culture were loosely stoppered and placed at random in a Gallenkamp Illuminated Orbital Incubator. The cultures were incubated, without media renewal for 72 hours under continuous illuminatioon of approximately 7000 lux. The temperature was maintained at 24 ± 1°C and gaseous exchange and suspension of the algal cells was ensured by the action of the orbital shaker oscillating at 100 cycles per minute. - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
- Test temperature:
- 23.9 - 24.2°C
- pH:
- 7.5 - 10.2
- Nominal and measured concentrations:
- Nominal: 5.5, 11, 22, 44, 87.9 mg enzyme concentrate dry matter/L
- Details on test conditions:
- TEST SYSTEM
- Test vessel: Conical flasks (250 mL)
- Type (delete if not applicable): loosely stoppered
- Material, size, fill volume: glas, 250 mL, 100 mL
- Initial cells density: 8.2*10^4 cells/mL
- Control end cells density: 2.4*10^6 cells/mL
- No. of vessels per concentration (replicates): 3
- No. of vessels per control (replicates): 6
GROWTH MEDIUM
- Standard medium used: yes
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: reverse-osmosis purified water
- Culture medium different from test medium: no
OTHER TEST CONDITIONS
- Sterile test conditions: yes
- Adjustment of pH: no
- Photoperiod: continuous illumination
- Light intensity and quality: 7000 lux provided by 7 x 30 W "warm white" 1 metre fluorescent tubes
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- Determination of cell concentrations: Samples were taken at 0, 24, 48 and 72 hours and the absorbance measured at 665 nm using 4 cm cell path cuvettes in a Cecil 373 Series 2 Spectrophotometer. The cell densities of the control cultures at initiation and at termination were determined by direct counting with the aid of a haemocytometer (Improved Neubauer).
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 2
- Test concentrations: 5.5, 11, 22, 44, 87.9 mg enzyme concentrate dry matter/L - Reference substance (positive control):
- no
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 43.1 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- other: enzyme concentrate dry matter
- Basis for effect:
- growth rate
- Key result
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 22 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- other: enzyme concentrate dry matter
- Basis for effect:
- growth rate
- Details on results:
- - Exponential growth in the control (for algal test): yes
- Observation of abnormalities (for algal test): There were no abnormalities in the control cultures or any of the test cultures apart from the two highest exposure levels (44, 87.9 mg enzyme concentrate dry matter/L), where cells were observed to be smaller than average and clumped.
- Any stimulation of growth found in any treatment: no - Conclusions:
- The toxicity of the test substance was not tested, however, a read-across was performed to Alpha-amylase.
Alpha-amylase, batch PPA4048 was inhibitory to the growth of Desmodesmus subspicatus. The ErC50 (24-72h) was 43.1 mg enzyme concentrate dry matter/L 5.2 mg active enzyme protein/L. NOEC for the 24 -72 hour growth rate was 22 mg enzyme concentrate dry matter/L. EbC50 (72h) was 21.1 mg enzyme concentrate dry matter/L. - Executive summary:
The toxicity of the test substance was not tested, however, a read-across was performed to Alpha-amylase.
A study was conducted to assess the inhibitory effect of Alpha-amylase on the growth of the unicellular green alga Desmodesmus subspicatus, Strain No. CCAP 276/20.
The study was conducted in accordance with OECD Guideline for Testing of Chemicals No. 201 and EEC Methods for the Determination of Ecotoxicity, EEC Directive 67/458 Annex VIII, Part C (87/302/EEC).
Algal cultures exposed to five test concentrations of Alpha-amylase plus one untreated control were incubated on an orbital shaker under continuous illumination at 24 ± 1°C for 72 hours. Growth was monitored daily by measuring the absorbance of each culture at 665 nm.
The following values were derived from the data:
ErC50(24-72h): 43.1 mg enzyme concentrate dry matter/L (equivalent to 5.2 mg active enzyme protein/L)
EbC50(72h): 21.1 mg enzyme concentrate dry matter/L
NOEC for the 24 -72 hour growth rate: 22 mg enzyme concentrate dry matter/L
NOEC 72h for AUC (Area under the curve): 11 mg enzyme concentrate dry matter/L
Reference
Description of key information
1,4 -alpha-glucan branching enzyme wa not tesed with algae, however, read-across was performed with a sensitive species to alpha-amylase.
Alpha-amylase, batch PPA4048 was inhibitory to the growth of Desmodesmus subspicatus. The ErC50 (24-72h) was 43.1 mg enzyme concentrate dry matter/L, equvalent to 5.2 mg active enzyme protein/L. NOEC for the 24 -72 hour growth rate was 22 mg enzyme concentrate dry matter/L. EbC50 (72h) was 21.1 mg enzyme concentrate dry matter/L.
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 5.2 µg/L
Additional information
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.
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