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EC number: 203-750-9 | CAS number: 110-26-9
- 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
- Endpoint:
- toxicity to aquatic algae and cyanobacteria
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- April, 2016
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 016
- Report date:
- 2017
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Alga, Growth Inhibition Test)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- N,N'-methylenediacrylamide
- EC Number:
- 203-750-9
- EC Name:
- N,N'-methylenediacrylamide
- Cas Number:
- 110-26-9
- Molecular formula:
- C7H10N2O2
- IUPAC Name:
- N,N'-methylenediacrylamide
- Test material form:
- solid: crystalline
- Details on test material:
- Purity = 99.8%
Constituent 1
- Specific details on test material used for the study:
- Test item identification : N,N'-Methylenediacrylamide
Batch number : LQ27A1696
Internal number : 2926879-001
Manufacturing date : January 14, 2016
Expiry date : January 13, 2017
Chemical name : N,N'-Methylenediacrylamide
C.A.S. number : 110-26-9
EEC number : 203-750-9
Molecular weight : 154.17 g/mol
Empirical formula : C7H10N2O2
Purity : > 99%
Sampling and analysis
- Analytical monitoring:
- yes
Test solutions
- Vehicle:
- yes
- Details on test solutions:
- The test concentration was chosen in accordance with the results of pre-tests (range-finding tests), whose relevant Raw Data were archived under the code of the present study.
The main test included only one test item concentration equal to 100.0 mg test item/L, corresponding to 99.8 mg/L as a.i. (calculated considering test item purity, 99.8% w/w, as reported in Certificate of Analysis supplied by the Sponsor).
The test medium was prepared as follows:
Prior to the test start, 500 mL of a 100.0 mg test item/L stock solution was prepared by direct weighing into algal culture medium (0.0500 g of test item into 500 mL of algal culture medium).
The obtained solution showed insolubilized flakes of test item, so it was sonicated for about 5 minutes. After sonication, it was clear and transparent.
A negative control with algal growth medium only was also tested
Test organisms
- Test organisms (species):
- Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
- Details on test organisms:
- The study was performed with the unicellular, fresh-water green algae Pseudokirchneriella subcapitata strain (formerly known as Selenastrum capricornutum), cultured in the laboratories of the Test Facility and originally purchased from the Institute of Plant Physiology of the University of Göttingen, Germany.
The algae were cultured in a climatic chamber at 24 °C ± 2 °C under continuous uniform illumination in the range 4440 - 8880 Lux in the spectral range 400-700 nm. The culture medium was the same of the test medium; the stock cultures were weekly transferred to fresh medium and maintained in continuous shaking to ensure the necessary amount of CO2and to keep algae in suspension. Cultures containing deformed or abnormal cells were discarded. Only exponentially growing algal cultures have been used to start the test.
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 72 h
Test conditions
- Test temperature:
- 24.0 – 24.1 °C.
- pH:
- 7.82 – 7.96 at the test start.
9.14 – 9.23 at the test end. - Nominal and measured concentrations:
- In fresh solution the analytical recovery was 97.9% of the nominal concentration (100 mg/L).
In spent solution (after 72 hours of exposure) the analytical recovery of the concentration was 102.0% of the nominal value.
Since the analytical recoveries of N,N'-Methylenediacrylamide were in the range 80 % - 120 %, the toxic end-points were calculated in terms of nominal test item concentrations (100 mg/L). - Details on test conditions:
- The treatment vessels were identified by experiment number, group and replicate number.
All the described procedures were conducted under a laminar flow bench to ensure the sterility of the algal cultures.
For the negative control and for the test concentrations, 100 mL capacity conical glass flasks capped with air permeable stoppers were used.
Six replicates for the test item concentration and six for negative control were prepared. At test start, 50 mL of test solutions were poured into the test flasks and inoculated with algae to obtain a starting cell density of about 104 cells/mL.
The algal inoculum was taken from a pre-culture, started 3 days before the beginning of the test in order to ensure that the assay was performed with exponentially growing algal population. The cell density of the inoculum was around 106 cells/mL.
The test flasks were incubated in a climatic chamber, under continuous illumination and constant shaking. The flasks were randomly distributed under the light and were replaced every day during the test.
Temperature:
The incubation temperature was continuously monitored during the course of the study by a PT100 probe installed in the environmental test chamber. It was between 24.0 – 24.1°C during the exposure period with a standard deviation of 0.02°C. The temperature range provided by OECD guideline is 24 ± 2 C. The temperature values during the test were within the provided range.
Light conditions:
Continuous illumination; light intensity was ranged between 6098 and 6250 Lux, within the OECD recommended range (4440 - 8880 Lux).
Test duration: 72 hours
Test medium:
Reconstituted water according to OECD Guideline 201.
Test medium pH was measured with a portable pH meter at the beginning and at the end of the test. For fresh solutions, the pH values were measured sampling an aliquot immediately after test solution preparation, before pouring it in the test flasks. For spent solutions (after 72 hours), pH were measured in each test flask. - Reference substance (positive control):
- yes
Results and discussion
Effect concentrationsopen allclose all
- Key result
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Key result
- Duration:
- 72 d
- Dose descriptor:
- NOEC
- Effect conc.:
- 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- biomass
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- The toxicity of N,N'-Methylenediacrylamide was determined in a GLP guideline study on Pseudokirchneriella subcapitata. The NOEC at 72 hours was 100 mg/L (limit test).
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