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EC number: 219-199-2 | CAS number: 2386-52-9
- 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
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: GLP unknown, non-guideline, experimental study, acceptable with restrictions
Data source
Reference
- Reference Type:
- publication
- Title:
- Toxicity of silver to two freshwater algae, Chlamydomonas reinhardtii and Pseudokirchneriella subcapitata, grown under continuous culture conditions: influence of thiosuphate.
- Author:
- Hiriart-Baer V, Fortin C, Lee D-Y, Campbell PGC.
- Year:
- 2 006
- Bibliographic source:
- Aquatic Toxicology 78:136-148
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Batch cultures of C. reinhardtii in exponential growth were transferred to turbidostats. For each turbidostat unit, the growth rate was determined for 1 day in control (Ag-free) medium and this rate was used as the reference growth rate. After this initial period, 110mAg was added to the culture chamber and to the influent medium to obtain a nominal Ag concentration of 10 nM. The algal growth rate was monitored, and once it had stabilized (normally within 18-24 h) the Ag concentration was increased to 20 nM in both the culture medium and the influent medium. Algal growth rates were monitored as before and a stepwise increase in Ag concentration was carried out in the sequence 10, 20, 30, 50 and 80 nM Agtot. For each replicate, an aliquot of 70 ml of the culture medium from the turbiostat culture was collected at the end of each exposure period (i.e., at ~ 18 - 24 h intervals) and this volume was then used for a series of analyses: total Ag; dissolved Ag, intracellular Ag; cell density and size; chlorophyll-a concentrations; cellular carbon, nitrogen and sulphur contents and medium pH.
- GLP compliance:
- not specified
Test material
- Reference substance name:
- Silver methanesulphonate
- EC Number:
- 219-199-2
- EC Name:
- Silver methanesulphonate
- Cas Number:
- 2386-52-9
- Molecular formula:
- CH4O3S.Ag
- IUPAC Name:
- silver methanesulphonate
- Test material form:
- solid
impurity 1
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
Not applicable
Sampling and analysis
- Analytical monitoring:
- yes
- Details on sampling:
- 70 ml samples of culture medium both exposure conentrations and control at end of each exposure period.
Test organisms
- Test organisms (species):
- Chlamydomonas reinhardtii
- Details on test organisms:
- Test organisms (species) Chlamydomonas reinhardtii (UTCC 11)
Details on test organisms - source University of Toronto Culture Collection
Details on test organisms - holding conditions prior to test Batch cell cultures maintained axenically in 100 ml of modified high salt medium at an ionic strength of 6 meq l-1. Maintenance batch cultures were grown in 250 ml polycarbonate Erlenmeyer flasks under constant illumination of 100 ± 10 μEm-1 s-1 with rotary agitation at 50 rpm at 20ºC. Cultures maintained weekly by transferring ~ 2 ml of culture to fresh, sterile medium (pH7; no pH buffers). Culture media autoclaved prior to addition of a filter-sterilized trace metal mix to avoid potential metal precipitation at high temperature.
Details on test organisms - life stage of test species used Exponential growth phase
Study design
- Test type:
- flow-through
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 24 h
- Remarks on exposure duration:
- 18-24 hrs at each concentration
- Post exposure observation period:
- Not applicable
Test conditions
- Hardness:
- no data
- Test temperature:
- 20°C
- pH:
- pooled effluent pH across all treatments 7 ± 0.3 (6.7 - 7.5; min-max)
- Dissolved oxygen:
- no data
- Salinity:
- not applicable
- Nominal and measured concentrations:
- Dissolved Ag concentrations measured in the turbidostat effluent were less than the total concentrations in the effluent, reflecting uptake of silver by the growing algal biomass; the % dissolved Ag varied between 50 and 85%, according to the influent concentration, the algal growth rate and the algal species. To evaluate Ag concentration algae exposed to in the turbidostats, free Ag+ in the effluent stream was calculated. The exposure medium was considered to contain no appreciable Ag binding ligands. The authors suggest that the EC50s values calculated from the free Ag+ concentrations in the effluent probably overestimated silver toxicity (underestimate EC50) since Ag+ in the effluent was measured after filtration and subsequent control experiments indicated that some adsorptive loss of Ag onto the filters could have occurred.
- Details on test conditions:
- TEST SYSTEM
Test vessel: Turbidostats - custom-made units consisting of a 1 l polycarbonate jar with an inserted pair of quartz cylinders containing an emitting and a detecting probe (λ = 910 nm, pulsed at 1 kHz and integrated over 2.3s). When measured turbidity exceeded set threshold value, a perstaltic pump was triggered to dilute the culture medium (10 ml min-1) and remove an equivalent volume (inlet and outlet tubes were placed at the bottom and surface of the culture vessel, respectively).
3 replicates per concentration
OTHER TEST CONDITIONS
- Sterile test conditions: yes
DETERMINATION OF GROWTH RATE: From medium replacement volume for a given time period.
TEST CONCENTRATIONS
Stepwise increment, 10, 20, 30, 50 and 80 nM Ag. - Reference substance (positive control):
- no
Results and discussion
Effect concentrations
- Key result
- Duration:
- 24 h
- Dose descriptor:
- EC10
- Effect conc.:
- 0.54 µg/L
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- element (dissolved fraction)
- Remarks:
- Silver
- Basis for effect:
- growth rate
- Remarks on result:
- other: recalculated from author's data
- Details on results:
- no data
- Results with reference substance (positive control):
- not applicable
- Reported statistics and error estimates:
- Student t-test with Bonferroni correction was used to make pairwise comparisons of the batch culture growth data. ANOVA used for effects of Ag treatments on growth rates and chemical composition. All statistical analyses carried out using Systat V.10. Significance set at p = 0.05.
Applicant's summary and conclusion
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The EC10 of silver to Chlamydomonas reinhardtil, recalulated from the author's data, is 0.54 µg/L.
- Executive summary:
The toxicity of silver toChlamydomonas reinhardtilwas assessed in continuous algal cultures grown in turbidostats, with a stepwise increaments of the silver concentration.
The EC10 of the test substance toChlamydomonas reinhardtil, recalulated from the author's data, is 0.54 µg/L.
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