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EC number: 412-780-3 | CAS number: 1380226-46-9 ADDITIV 104
- 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:
- 7 November 2002 to 11 November 2002
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP compliant guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 002
- Report date:
- 2002
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Alga, Growth Inhibition Test)
- GLP compliance:
- yes
Test material
- Reference substance name:
- Reaction product of ammonium molybdate and C12-C24-diethoxylated alkylamine (1:5-1:3)
- EC Number:
- 412-780-3
- EC Name:
- Reaction product of ammonium molybdate and C12-C24-diethoxylated alkylamine (1:5-1:3)
- Cas Number:
- 1380226-46-9
- Molecular formula:
- A complex mixture of species so no unique molecular formula can be given
- IUPAC Name:
- dimolybdenum(6+) diammonium 2-{2-[(octadec-9-en-1-yl)amino]ethoxy}ethan-1-ol heptaoxidandiide
- Test material form:
- liquid: viscous
- Details on test material:
- - Name of test material (as cited in study report): ADDITIV 104
- Physical state: dark red liquid
- Lot/batch No.: 651010903
- Storage condition of test material: room temperature, in the dark
Constituent 1
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
Not reported
Sampling and analysis
- Analytical monitoring:
- yes
- Details on sampling:
- The concentration and stability of the test material in the test preparations were verified by chemical analysis at 0 and 72 hours.
Test solutions
- Vehicle:
- no
- Details on test solutions:
- Due to the low aqueous solubility and complex nature of the test material for the purposes of the definitive test the test material was prepared as a Water Accommodated Fraction (WAF).
Using syringes amounts of test material (125, 250, 500, 1000 and 2000 mg) were each separately added onto the surface of 10 litres of culture medium to give the 12.5, 25, 50, 100 and 200 mg/l loading rates respectively. These were then stirred for 23 hours using a stirring rate such that a
dimple was formed at the media surface. The stirring was stopped after 23 hours and the mixtures allowed to stand for 1 hour. A small amount of each WAF was then removed and checked for the presence of micro-dispersions or globules of test material. As globules/micro-dispersions of test
material were observed to be present it was considered appropriate to remove the aqueous phase or WAF by filtration through a glass wool plug.
A glass tube, covered at one end with paraflim was submerged into the vessel, sealed end down, to a depth of approximately 5 cm from the bottom ofthe vessel. A length of Tygon tubing was then inserted into the glass tube and pushed through the parafilm seal. At the opposite end of the
Tygon tubing a glass wool plug was inserted (approximately 2-4 cm in length) to trap any micro-dispersions. The aqueous phase or WAF was then removed by filtration through the glass wool plug (the first 75-100 ml discarded) and used for testing.
Microscopic examination of the WAFs after filtration through a glass wool plug showed there to be no globules/micro-dispersions of test material present.
An aliquot (700 ml) of each of the WAFs was separately inoculated with algal suspension (3.5 ml) to give the required test concentrations of 12.5, 25, 50, 100 and 200 mg/l loading rate WAF.
The concentration and stability of the test material in the test preparations were verified by chemical analysis at 0 and 72 hours
Test organisms
- 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 Collection of Algae and Protozoa (CCAP), Institute of Freshwater Ecology, The Ferry House, Far Sawrey, Ambleside, Cumbria
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72
- Post exposure observation period:
- None
Test conditions
- Hardness:
- Not reported
- Test temperature:
- Temperature was maintained at 24 ± 1°C throughout the test.
- pH:
- Test start: 7.7
Test end: 8.5
The pH of each control and test flask was determined at initiation of the test and after 72 hours exposure. The pH was measured using a WTW pH 320 pH meter - Dissolved oxygen:
- Not reported
- Salinity:
- Not reported
- Nominal and measured concentrations:
- Water Accommodated Fractions (WAFs) of the test material over a range of nominal loading rates of 12.5, 25, 50, 100 and 200 mg/l
- Details on test conditions:
- TEST SYSTEM
- Test vessel: 250 ml glass conical flasks plugged with polyurethane foam bungs to reduce evaporation.
- Aeration: constant
- Initial cells density: Pre-culture conditions gave an algal suspension in log phase growth characterised by a cell density of 2.06 x 106 cells per ml. Inoculation of 700 ml of test medium with 3.5 ml of this algal suspension gave an initial cell density of 10 cells per ml and had no significant dilution effect.
- No. of vessels per concentration (replicates): 3
- No. of vessels per control (replicates): 3
CULTURE MEDIUM
NaNO3 25.5 mg/l
MgC12.6H20 12.164 mg/l
CaCI2.2H20 4.41 mg/l
MgSO4.7H20 14.7 mg/l
K2HPO4 1.044 mg/l
NaHCO3 15.0 mg/I
H3B03 0.1855 mg/l
MnCi2.4H20 0.415 mg/l
ZnC12 0.00327 mg/l
FeCi3.6H20 0.159 mg/l
CoC12.6H20 0.00 143 mg/l
Na2MoO4.2H20 0.00726 mg/l
CuC12.2H20 0.000012 mg/l
Na2EDTA.2H20 0.30 mg/l
Na2SeO3.5H20 0.000010 mg/I
The cuiture medium was prepared using reverse osmosis purified deionised water (Elga Optima 15+) and the pH adjusted to 7.5 ± 0.1 with 0.1N NaOH or HCl. The prepared media was sterilised by 0.2 micron membrane flitration
OTHER TEST CONDITIONS
- Photoperiod: continuous illumination
- Light intensity and quality:approximately 7000 lux
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- Determination of cell concentrations: Samples were taken at 0, 24, 48 and 72 hours and the cell densities determined using a Coulter®
Multisizer II Particle Counter.
- Range finding study: Yes
- Results used to determine conditions for the definitive test: Yes
TEST CONCENTRATIONS
- Range finding study
- Test concentrations (Initial range finding test): Water Accommodated Fractions (WAFs) of the test material, nominal loading rates of 100 and 1000 mg/l
- Test concentrations (Second range finding test): Water Accommodated Fractions (WAFs) of the test material over a range of nominal loading rates of 1.0, 10 and 100 mg/l
- Results used to determine the conditions for the definitive study: Yes - Reference substance (positive control):
- no
Results and discussion
Effect concentrations
- Duration:
- 72 h
- Dose descriptor:
- NOELR
- Effect conc.:
- >= 12.5 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Details on results:
- The effect of the test material on the growth of Scenedesmus subspicatus has been investigated over a 72-Hour period and gave an EbL*50 (72 h) value of 26 mg/l loading rate WAF; 95% confidence limits 22 -31 mg/l loading rate WAF and an ErL*50 (0 - 72 h) value of 56 mg/l loading rate WAF;95% confidence limits 50-62 mg/l loading rate WAF.
The No Observed Effect Loading rate at 72 hours was 12.5 mg/l loading rate WAF
Any other information on results incl. tables
Inhibition of Growth Rate and Biomass
|
[Increase in growth as compared to the controls] EbL50(72 h) from Figure 2 = 26 mg/l loading rate WAF
Erl50(0 - 72 h) from Figure 2 =56 mg/1 loading rate WAF
Applicant's summary and conclusion
- Conclusions:
- The No Observed Effect Loading rate (NOELR) at 72 hours was calculated to be 12.5 mg/l loading rate WAF.
- Executive summary:
In a GLP compliant, guideline 72 hour acute toxicity test to aquatic algal species Scenedesmus subspicatus the test substance gave an EbL*50 (72 h) value of 26 mg/l loading rate WAF; 95% confidence limits 22 -31 mg/l loading rate WAF and an ErL*50 (0 - 72 h) value of 56 mg/l loading rate WAF; 95% confidence limits 50 -62 mg/l loading rate WAF.
The No Observed Effect Loading rate at 72 hours was 12.5 mg/l loading rate WAF.
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